Member State report / Art11 / 2014-2020 / D2 / Estonia / Baltic Sea
| Report type | Member State report to Commission |
| MSFD Article | Art. 11 Monitoring programmes (and Art. 17 updates) |
| Report due | 2014-10-15; 2020-10-15 |
| GES Descriptor | D2 Non-indigenous species |
| Member State | Estonia |
| Region/subregion | Baltic Sea |
| Reported by | Estonian Environment Agency |
| Report date | 2014-09-25; 2020-11-11 |
| Report access |
2014 data
2020 data
| Monitoring programme | Monitoring programme name | MP_D2 |
|---|---|---|
| Monitoring programme | Reference existing programme | |
| Monitoring programme | Marine Unit ID | |
| Q4e - Programme ID | BALLT-D012-7 |
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| Q4f - Programme description |
Monitoringo programa vertina svetimkraščių rūšių aptikimą ir gausumą ir poveikį vietinei ekosistemai. Jūros Strategijos Pagrindų Direktyvos (Directive 2008/56/EC) rodiklių vertinime turėtų būti įtrauktos pagrindinės jūros organizmų grupės (zoo- ir fitoplanktonas, zoo- ir fitobentosas, žuvys, paukščiai, žinduoliai), šių rodiklių monitoringo programa ženkliai persidengia su kitų rodiklių stebėsena. Šiuo metu vykdoma nevietinių rūšių stebėsena vykdoma remiantis Valstybinės aplinkos monitoringo programos rezultatais. Kitiems rodikliams (pvz., bioįvairovei, eutrofikacijai) vertinti surinkti duomenys gali būti naudojami naujų nevietinių rūšių skaičiaus kaitos tendencijai nustatyti bei biotaršos indeksui įvertinti.
Papildomas nevietinių rūšių monitoringas Lietuvos Baltijos jūros priekrantėje planuojamas vykdyti remiantis Helsinkio komisijos nevietinių rūšių biologinio monitoringo ir uostų stebėsenos protokolų studijomis (HELCOM 2013). Papildomi stebėjimai reikalingi norint kokybiškai įvertinti GAB rodiklį, papildoma nevietinių rūšių stebėjimo (monitoringo) programa planuojama kietų substratų ir uosto akvatorijoje.
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| Q5e - Natural variability |
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| Q5d - Adequacy for assessment of GES | Q5d - Adequate data | N |
| Q5d - Adequacy for assessment of GES | Q5d - Established methods | N |
| Q5d - Adequacy for assessment of GES | Q5d - Adequate understanding of GES | N |
| Q5d - Adequacy for assessment of GES | Q5d - Adequate capacity | Y |
| Q5f - Description of programme for GES assessment |
a. Program not fully address assessment needs, more information is needed about IAS occurence, abundance and distribution.
b. Esamų vietų išdėstymas nepakankamai apima vertinamos akvatorijos gamtinių sąlygų įvairovę bei galimas atplitusių nevietinių rūšių pradinio įsikūrimo vietas. Rodiklis yra siūlomas vertinti ilgesniam laikotarpiui (kas 10 metų), esamas matavimų dažnis yra pakankamas adekvačiam rodiklio įvertinimui.
c. Rodiklis labai priklauso nuo tyrimų intensyvumo ir nevietinių rūšių inventorizacijos pastangų. Kai kurios rūšys gali egzistuoti ekosistemoje nepastebėtos pakankamai ilgą laiką. Kai kurių taksonominių grupių (pvz., Oligochaeta, Ostracoda) identifikavimo rezoliucija neleidžia vykdyti efektyvią naujai atplitusių rūšių apskaitą.
d. Rodiklis tiesiogiai priklauso nuo naujų rūšių atsiradimo ekosistemoje, tačiau poveikio ekosistemai neatspindi. Nevisos atvykusios rūšys turi vienodą įsikūrimo tikimybę, ir labai sunku iš atplitusių rūšių skaičiaus nuspėti kiek ir kokios jų taps invazinėmis ir turės reikšmingos įtakos ekosistemai. Rodiklio taikymas paremtas prielaida, kad kuo daugiau plinta nevietinių rūšių, tuo didesnė tikimybė, kad dalis jų taps invazinės.
e. Does not respond to risks of not achieving GES
Daugiau informacijos pdf ataskaitoje, 22-27 psl.
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| Q5g - Gap-filling date for GES assessment | After2020 |
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| Q5h - Plans to implement monitoring for GES assessment |
Siekiant adekvačiai įvertinti rodiklį, planuojama stebėsenos stotis papildyti tyrimų vietomis uosto akvatorijoje. Atsižvelgiant į turimus duomenis, nevietinių rūšių ekologines charakteristikas ir galimus jų plitimo kelius, pasiūlytos nevietinių rūšių stebėsenai papildomos stotys Klaipėdos uosto akvatorijoje: papildomas stebėjimas numatomas (kieto dugno zoo- ir fitobentosui, zoo- ir fitoplanktonui, minkšto dugno zoobentosui, judriems epifaunos organizmams). Pagautų individų laboratorinė analizė atliekama pagal nustatytas HELCOM rekomendacijas (HELCOM 2013).
Paraleliai su mėginių ėmimu planuojama nustatyti pagrindinius aplinkos parametrus (temperatūra, druskingumas, Secchi gylis, chlorofilas „a“, organinės medžiagos kiekis vandenyje ir nuosėdose, nuosėdų tipas, granulometrinė sudėtis).
Numatomas stebėsenos planas:
2016 metai – parengta jūrų uostų stebėjimo (monitoringo) tvarka;
2018 metai – vertinimo metodikos atnaujinimas;
2020 metai – stebėsenos metodikos parengimas/įteisinimas;
2021 metai - uosto monitoringo pradžia
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| Q6a -Relevant targets | Q6a - Environmental target | 2 |
| Q6a -Relevant targets | Q6a - Associated indicator | 2.1.1 2.2.2 |
| Q6b - Adequacy for assessment of targets | Q6b_SuitableData | N |
| Q6b - Adequacy for assessment of targets | Q6b_EstablishedMethods | N |
| Q6b - Adequacy for assessment of targets | Q6d_AdequateCapacity | Y |
| Q6c - Target updating | N |
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| Q6d - Description of programme for targets assessment | According Lithuanian marine strategy Lithuanian monitoring programmes will be not able to achieve target only taking actions in national level, there is a need for regional cooperation, and only regional cooperation can help to evaluate and achieve national targets.
See page 238 in http://vanduo.gamta.lt/cms/index?rubricId=6dffaf28-c6a1-40cf-967f-b55ddaeeffda.
2015 metais bus atnaujinti tikslai ir susiję pažangos vertinimo rodikliai tuomet bus galima pakartotinai vertinti monitoringo rezultatų panaudojimą/adekvatumą. |
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| Q6e - Gap-filling date for targets assessment | After2020 |
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| Q6f - Plans to implement monitoring for targets assessment | Programme will be checked against increased knowledge about risks and impacts. |
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| Q7a - Relevant activities |
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| Q7b - Description of monitoring of activities |
Yra žinoma, kad pagrindiniai keliai, kuriais nevietiniai vandens organizmai patenka į Lietuvos jūrinę ekosistemą – tai atsitiktinės introdukcijos su laivais arba vandens kanalais, savaiminis rūšių plitimas iš kaimyninių šalių bei tikslinės introdukcijos. Pagrindine nevietinės rūšys atsiranda dėl uosto veiklos, laivybos.
Esamų vietų išdėstymas nepakankamai apima vertinamos akvatorijos gamtinių sąlygų įvairovę bei galimas atplitusių nevietinių rūšių pradinio įsikūrimo vietas. Siekiant adekvačiai ir kokybiškai įvertinti rodiklį, esamos stebėsenos stotys visų pirma turi būti papildytos tyrimų vietomis uosto akvatorijoje.
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| Q7c - Relevant measures | ||
| Q7e - Adequacy for assessment of measures | Q7d - Adequate data | N |
| Q7e - Adequacy for assessment of measures | Q7d - Established methods | Y |
| Q7e - Adequacy for assessment of measures | Q7d - Adequate understanding of GES | N |
| Q7e - Adequacy for assessment of measures | Q7d - Adequate capacity | Y |
| Q7e - Adequacy for assessment of measures | Q7d - Addresses activities and pressures | Y |
| Q7e - Adequacy for assessment of measures | Q7d - Addresses effectiveness of measures | Y |
| Q7d - Description of monitoring for measures | The monitoring programme gives quantitative and qualitative information on the abundance and characteristics of non-indigenous species in the Lithuanian Baltic sea coast. Using national accepted measures and indexes we have insights in the effectiveness of current and future measures of non-indigenous species in Lithuanian coast. |
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| Q7f - Gap-filling date for activities and measures | After2020 |
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| Q8a - Links to existing Monitoring Programmes |
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| Reference sub-programme | Sub-programme ID | |
| Reference sub-programme | Sub-programme name | Non-indigenous species - abundance and/or biomass |
| Q4g - Sub-programmes | Sub-programme ID | |
| Q4g - Sub-programmes | Sub-programme name | Non-indigenous species - abundance and/or biomass |
| Q4k - Monitoring purpose | ||
| Q4l - Links of monitoring programmes of other Directives and Conventions | ||
| Q5c - Features | Q5c - Habitats |
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| Q5c - Features | Q5c - Species list |
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| Q5c - Features | Q5c - Physical/Chemical features |
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| Q5c - Features | Q5c - Pressures |
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| Q9a - Elements | ||
| Q5a - GES criteria | Relevant GES criteria |
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| Q5b - GES indicators | Relevant GES indicators |
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| Q9b - Parameters monitored (state/impact) | Species distribution | |
| Q9b - Parameters monitored (state/impact) | Species population size | |
| Q9b - Parameters monitored (state/impact) | Species population characteristics | |
| Q9b - Parameters monitored (state/impact) | Species impacts | |
| Q9b - Parameters monitored (state/impact) | Habitat distribution | |
| Q9b - Parameters monitored (state/impact) | Habitat extent | |
| Q9b - Parameters monitored (state/impact) | Habitat condition (physical-chemical) | |
| Q9b - Parameters monitored (state/impact) | Habitat condition (biological) | |
| Q9b - Parameters monitored (state/impact) | Habitat impacts | |
| Q9b - Parameters monitored (pressures) | Pressure input | |
| Q9b - Parameters monitored (pressures) | Pressure output | |
| Q9b - Parameters monitored (activity) | Activity | |
| Q9b Parameters monitored (other) | Other | |
| Q41 Spatial scope | ||
| Q4j - Description of spatial scope | ||
| Marine Unit IDs |
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| Q4h - Temporal scope | Start date- End date | - |
| Q9h - Temporal resolution of sampling | ||
| Q9c - Monitoring method | ||
| Q9d - Description of alteration to method | ||
| Q9e - Quality assurance | ||
| Q9f - Quality control | ||
| Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | |
| Q9g - Spatial resolution of sampling | Q9g - No. of samples | |
| Q9i - Description of sample representivity | ||
| Q10a - Scale for aggregation of data | ||
| Q10b - Other scale for aggregation of data | ||
| Q10c - Access to monitoring data | Q10c - Data type | |
| Q10c - Access to monitoring data | Q10c - Data access mechanism | |
| Q10c - Access to monitoring data | Q10c - Data access rights | |
| Q10c - Access to monitoring data | Q10c - INSPIRE standard | |
| Q10c - Access to monitoring data | Q10c Date data are available | |
| Q10c - Access to monitoring data | Q10c - Data update frequency | |
| Q10d - Description of data access | ||
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Monitoring strategy description |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
The aim of the monitoring strategy "SD2 - Non-indigenous species" is to assess the introduction and status of non-indigenous species in the pelagic and benthic realm through collection of data on their occurrence, abundance/biomass, distribution and ecological impacts. The monitoring is aimed at characterising the anthropogenic pressure and associated impacts, but the gathered data and information also allows to characterise the state of the marine environment. As shipping (ballast water and sediments) is the major introduction vector for marine non-indigenous species, monitoring is established in major ports and adjacent areas to them. Monitoring includes phytoplankton, zooplankton, phytobenthos, zoobenthos and fish. In addition, species-specific monitoring covers a few most invasive non-indigenous species, such as the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. Data from the following monitoring programmes are exploited in this monitoring strategy: "Non-indigenous species – harbours and adjacent regions", "Non-indigenous species – abundance and biomass", "Phytoplankton species composition, abundance and biomass", "Zooplankton species composition, abundance and biomass", "Macrozoobenthos", "Phytobenthic communities", "Coastal fish" and "Off-shore fish". The main anthropogenic activities and associated pressures are dealt with in the programme "Marine and coastal activities". |
Coverage of GES criteria |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
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 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 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 was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Adequate monitoring was in place in 2014 |
Gaps and plans |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Potential pathways of introduction as Sillamäe and Paldiski harbours, leisure craft (hull fouling) and aquaculture are not covered by monitoring yet. There is no regular monitoring of certain groups of non-indigenous species (microorganisms and parasites), but done by research projects. The frequency of zooplankton monitoring is low. The same applies to phytoplankton in case of monitoring of phytoplankton non-indigenous species. The monitoring of mobile epifauna (demersal fish, marine invertebrates) needs to be extended. |
Related targets |
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Coverage of targets |
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 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 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 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 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 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 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 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 is in place by July 2020 |
Adequate monitoring is in place by July 2020 |
Related measures |
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Coverage of measures |
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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Related monitoring programmes |
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Programme code |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D00-40_MarineAndCoastalActivities |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-7_FishCoastal |
BALEE-D010403-8_FishOffshore |
BALEE-D010403-8_FishOffshore |
BALEE-D010403-8_FishOffshore |
BALEE-D010403-8_FishOffshore |
BALEE-D010403-8_FishOffshore |
BALEE-D010403-8_FishOffshore |
BALEE-D010403-8_FishOffshore |
BALEE-D010405-10_Phytop |
BALEE-D010405-10_Phytop |
BALEE-D010405-10_Phytop |
BALEE-D010405-11_Zoopl |
BALEE-D010405-11_Zoopl |
BALEE-D010405-11_Zoopl |
BALEE-D01040605-13_SeabedVegetationZone |
BALEE-D01040605-13_SeabedVegetationZone |
BALEE-D01040605-13_SeabedVegetationZone |
BALEE-D01040605-13_SeabedVegetationZone |
BALEE-D01040605-13_SeabedVegetationZone |
BALEE-D01040605-13_SeabedVegetationZone |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D01040605-14_Macrozoobenthos |
BALEE-D02-18_NISRiskAreas |
BALEE-D02-18_NISRiskAreas |
BALEE-D02-18_NISRiskAreas |
BALEE-D02-18_NISRiskAreas |
BALEE-D02-19_NISDynImpact |
BALEE-D02-19_NISDynImpact |
Programme name |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Marine and coastal activities |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Coastal fish |
Off-shore fish |
Off-shore fish |
Off-shore fish |
Off-shore fish |
Off-shore fish |
Off-shore fish |
Off-shore fish |
Phytoplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass |
Phytoplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Zooplankton species composition, abundance and biomass |
Phytobenthic communities |
Phytobenthic communities |
Phytobenthic communities |
Phytobenthic communities |
Phytobenthic communities |
Phytobenthic communities |
Macrozoobenthos |
Macrozoobenthos |
Macrozoobenthos |
Macrozoobenthos |
Macrozoobenthos |
Macrozoobenthos |
Macrozoobenthos |
Macrozoobenthos |
Macrozoobenthos |
Non-indigenous species – harbours and adjacent regions |
Non-indigenous species – harbours and adjacent regions |
Non-indigenous species – harbours and adjacent regions |
Non-indigenous species – harbours and adjacent regions |
Non-indigenous species – abundance and biomass |
Non-indigenous species – abundance and biomass |
Update type |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
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 |
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 |
Same programme as in 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Same programme as in 2014 |
Same programme as in 2014 |
Old programme codes |
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Programme description |
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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the coastal fish species and communities (Species composition of the group; Size, age and sex structure; fecundity, survival and mortality/injury rates; Habitat for the species (extent, suitability); Species abundance (numbers of individuals and/or biomass)). It provides data to monitoring strategy “SD1.4 Biodiversity – Fish”, „SD3–Commercially exploited fish“ and “SD4/SD1 Food webs / Biodiversity – ecosystems”, but also to “SD2– Non-indigenous species”. The program is regionally coordinated by HELCOM (partially also by ICES) and the HELCOM monitoring manual is followed. During the annual monitoring programme, all coastal fish species are included in the dataset, but special attention is directed towards economically significant or ecologically relevant key species (perch, flounder, pikeperch). Atlantic salmon is used as an indicator species for migratory (anadromous) fishes and is monitored in coastal waters and selected rivers (salmonid habitats). Monitoring of protected fish species under HD needs to be developed for the sea area as well.
The programme was modified from 2014 by adding migratory fishes that were as a separate sub-programme in 2014.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – population characteristics; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor the status of the commercially exploited pelagic fish species – sprat and herring in the offshore areas of the Estonian marine waters. The biomass and fishing mortality of stocks are assessed. It provides data to monitoring strategy “SD1.4 Biodiversity – Fish” and „SD3-commercially exploited fish“. Monitoring is conducted annually. The program is regionally coordinated via ICES and the ICES monitoring manual is followed.
The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – mortality/injury rates from fisheries (targeted and/or incidental). |
The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria.
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: Pelagic habitats – community characteristics. |
The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria.
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: Pelagic habitats – community characteristics. |
The aim of the programme is to monitor phytoplankton communities (species composition, abundance, biomass and seasonal cycle of dominant groups) in the water column. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD1.6 Biodiversity – pelagic habitats”, “SD4/SD1 Food webs / Biodiversity – ecosystems” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C2, Descriptor D1, Criterion D1C6 and Descriptor D4, Criterion D4C1. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM divisions) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency of 5 to 12 times a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The threshold values for the indicator of seasonal succession of dominating phytoplankton groups are still missing for some assessment units of the Baltic Sea (incl. Estonian marine area), mainly due to the lack of data corresponding to the set criteria.
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: Pelagic habitats – community characteristics. |
The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet.
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: Pelagic habitats – community characteristics. |
The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet.
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: Pelagic habitats – community characteristics. |
The aim of the programme is to monitor species composition, abundance and biomass of mesozooplankton. It provides data to monitoring strategy “SD1.6 Biodiversity – pelagic habitats”, as well as “SD2-Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptors D1, Criterion D1C6, Description D2 Criterions D2C1 and D2C2 and Descriptor D4 Criterion D4C2. Data are gathered to assess the state of the marine environment and environmental status in three coastal water bodies and all off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) as well as pressures from/by non-indigenous species. Monitoring is conducted yearly with a frequency 10 times a year at the designated coastal monitoring stations (3 stations in each coastal water body) and with frequency twice a year for 16 stations in the Estonian off-shore areas. The program is regionally coordinated via HELCOM and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). Mesozooplankton Mean Size Total Stock indicator is developed by HELCOM on the basis of mesozooplankton data. The threshold values for the indicator have been internationally agreed for some sub-basins, but not for the Gulf of Riga yet.
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: Pelagic habitats – community characteristics. |
The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor phytobenthic communities (species composition, coverage, abundance, biomass, depth distribution) along the depth gradient. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats” and “SD2– Non-indigenous species”. The programme is related to GES Descriptor D5, Criterion D5C6 and Criterion D5C7, Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM sub-divisions) in response to pressure levels. Monitoring is conducted in coastal waters yearly or at least once per six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body). The program is regionally partly coordinated via HELCOM and the HELCOM monitoring manual is followed (soft-bottom habitats). Data are yearly reported to the national environmental monitoring database KESE (by 1 March).
The programme corresponds to the following monitoring programmes in the indicative list: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor macrozoobenthos communities (species composition, abundance and biomass) on the seafloor. It provides data to monitoring strategy “SD5 – Eutrophication”, as well as “SD6/SD1 Sea-floor integrity/Biological diversity – benthic habitats”, “SD2– Non-indigenous species” and “SD4/SD1 Food webs / Biodiversity – ecosystems”. The programme is related to GES Descriptor D5, Criterion D5C8, Descriptor D2, Criteria D2C1, D2C2 and D2C3, Descriptor D4, Criterion D4C2 and Descriptor D6, Criterion D6C5. Data are gathered to assess spatial variability, temporal trends and environmental status in coastal water bodies and off-shore sub-basins of the Baltic Sea (HELCOM division) in response to pressure levels. Monitoring is conducted yearly or at least once in six years with a frequency once a year at the designated monitoring stations (at least 3 stations in each coastal water body and 11 in the Estonian off-shore areas). The program is regionally coordinated via HELCOM and the HELCOM monitoring manual is followed. The data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine).
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: Seabed habitats – community characteristics; Benthic species – abundance and/or biomass. |
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March).
The programme has been modified since 2014 by adding species-specific monitoring.
The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass. |
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March).
The programme has been modified since 2014 by adding species-specific monitoring.
The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass. |
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March).
The programme has been modified since 2014 by adding species-specific monitoring.
The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass. |
The aim of the programme is to monitor the occurrence and abundance/biomass of non-indigenous phytoplankton, zooplankton, macrozoobenthos and fish in harbours and adjacent areas. Port NIS monitoring is carried out in one port (Muuga) with the identified highest risk for introduction of new non-indigenous species, while monitoring of adjacent areas is performed for three harbours. In addition, species-specific monitoring covers a few most invasive non-indigenous species: the round goby Neogobius melanostomus, Chinese mitten crab Eriocheir sinensis and Harris mud crab Rhithropanopeus harrisii. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The monitoring, data collection and assessment quality are assured by regional coordination via HELCOM, including following the OSPAR/HELCOM port biological monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March).
The programme has been modified since 2014 by adding species-specific monitoring.
The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species inputs - from specific sources; Non-indigenous species - abundance and/or biomass. |
The aim of the programme is to cover all major organism groups (phyto/zooplankton, phyto/zoobenthos, fish) and monitor both, pelagic and benthic communities (abundance/biomass and proportion of non-indigenous species in zooplankton and macrozoobenthos communities, abundance/biomass of mobile species, and biopollution level index). Most of the data and information used originate from other monitoring strategies and programmes. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The assessment unit is the whole Estonian marine area. The monitoring and assessment quality is assured by regional coordination via HELCOM and following the HELCOM monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The threshold values for indicators required for MSFD assessments have been defined (nationally, except for the biopollution level).
The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species - abundance and/or biomass. |
The aim of the programme is to cover all major organism groups (phyto/zooplankton, phyto/zoobenthos, fish) and monitor both, pelagic and benthic communities (abundance/biomass and proportion of non-indigenous species in zooplankton and macrozoobenthos communities, abundance/biomass of mobile species, and biopollution level index). Most of the data and information used originate from other monitoring strategies and programmes. The programme provides data to monitoring strategy “SD2 – Non-indigenous species ”. The programme is primarily related to GES Descriptor D2, Criteria D2C1, D2C2 and D2C3; but also contributes to D1, D4 and D6. Monitoring is conducted annually at the designated monitoring stations with organism-group specific monitoring designs. The assessment unit is the whole Estonian marine area. The monitoring and assessment quality is assured by regional coordination via HELCOM and following the HELCOM monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March). The threshold values for indicators required for MSFD assessments have been defined (nationally, except for the biopollution level).
The programme corresponds to the following monitoring programmes in the indicative list: Non-indigenous species - abundance and/or biomass. |
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Regional cooperation - countries involved |
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Regional cooperation - implementation level |
Coordinated data collection |
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Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
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Coordinated data collection |
Coordinated data collection |
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Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
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Coordinated data collection |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
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Agreed data collection methods |
Coordinated data collection |
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Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
Coordinated data collection |
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Coordinated data collection |
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Monitoring details |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
Data on all coastal fish species are being collected annually in discrete monitoring areas within the national fisheries data collection programme (https://www.envir.ee/et/eesmargid-tegevused/kalandus/kalanduse-riiklik-andmekoguminen-programm-akp). |
For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database. |
For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database. |
For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database. |
For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database. |
For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database. |
For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database. |
For monitoring offshore fish species the hydro-acoustic surveys and scientific trawlings are carried out. In addition, ICES coordinated cruises (BIAS, BITS) are carried out and the data are submitted to the ICES database. |
Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual).
In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring. |
Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual).
In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring. |
Phytoplankton samples are collected with a bathometer at water depths of 1, 5 and 10 m together with samples of seawater chlorophyll a. An integrated sample is made pooling equal amounts of water collected from fixed depths. When the integrated sample is thoroughly mixed, a portion is poured into a clear glass bottle and fixed with preservation chemical for further transport, storage and analysis of the phytoplankton sample. As part of the Ferrybox monitoring, samples are collected with an automatic sampler from depths of 4-5 m from a predefined location on the route of the liner. Phytoplankton is analysed according to the relevant international standard methods (EN 16695: 2015, HELCOM Monitoring Manual).
In 3 coastal water bodies sampling is carried out annually 10-12 times per year (from April to October), Haapsalu coastal waterbody - 10-12 times every third year. Other coastal water bodies are monitored in rotation 6 times per year (from June to September) at least once during a 6-year period. In the off-shore areas the research vessel-based monitoring is conducted 5 times per year (from April to October) and 12 times every year in frames of Ferrybox monitoring. |
The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory. |
The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory. |
The samples are collected by means of vertical hauls using a Juday or WP-2 net with 0,1 mm mesh size. The collected samples are preserved in a formaldehyde solution to microscopic analysis to be performed in a laboratory. |
The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information. |
The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information. |
The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information. |
The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information. |
The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information. |
The presence of species, total coverage and maximum distribution depth are registered during visual observations or using underwater video remote observation method. In the monitoring site, the total coverage of phytobenthos, species presence and their coverage, as well as sediment type are observed. Quantitative samples are collected by a diver with the 20x20 metal frame (in triplicate) and deep-freezed for laboratory analysis. In the laboratory, the species composition and dry weight of each species per 1m2 are determined. In frames of coastal waters monitoring, the total nitrogen, total phosphorus (6x per year) and PAR and water temperature are also registered (continuous measurements during 3-month period) in each monitoring area as supplementary information. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
Macrozoobenthos samples are collected once a year in off-shore areas and designated coastal waters and in rotation at least once in a 6-year period from other coastal waters. Van Veen or Ekman type grab samplers are used for sampling. The sediment type, concentration of dissolved oxygen in the near-bottom layer, concentration of H2S, water temperature and salinity are registered as supplementary information at the sampling site. Every sample is collected in triplicate and frozen for laboratory analyse. In the laboratory, the species composition, abundance of species and dry weight of every species (per 1 m2) is determined.
For observation of maximum depth distribution of Limecola balthica, three designated transects are monitored in the open-sea area; samples (one sample per each depth point) are taken in accordance with the transect depth gradient. |
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations. |
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations. |
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations. |
The phytoplankton, mesozooplankton, zoobenthos, fouling, mobile epifauna and fish monitoring samples are collected in accordance with HELCOM and HELCOM/OSPAR guidelines from two ports and three adjacent areas. Information on NIS occurrence is also gathered from all biological monitoring stations. |
Most of the data and information used originate from other monitoring strategies and programmes. Information on NIS occurrence is gathered from all biological monitoring stations. |
Most of the data and information used originate from other monitoring strategies and programmes. Information on NIS occurrence is gathered from all biological monitoring stations. |
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Features |
Aquaculture – marine, including infrastructure
|
Fish and shellfish harvesting (professional, recreational)
|
Hunting and collecting for other purposes
|
Marine plant harvesting
|
Extraction of minerals (rock, metal ores, gravel, sand, shell)
|
Extraction of oil and gas, including infrastructure
|
Extraction of water
|
Military operations (subject to Article 2(2))
|
Transmission of electricity and communications (cables)
|
Renewable energy generation (wind, wave and tidal power), including infrastructure
|
Research, survey and educational activities
|
Coastal defence and flood protection
|
Offshore structures (other than for oil/gas/renewables)
|
Restructuring of seabed morphology, including dredging and depositing of materials
|
Tourism and leisure activities
|
Tourism and leisure infrastructure
|
Transport infrastructure
|
Transport – shipping
|
Waste treatment and disposal
|
Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events
|
Input of litter (solid waste matter, including micro-sized litter)
|
Input of nutrients – diffuse sources, point sources, atmospheric deposition
|
Input of anthropogenic sound (impulsive, continuous)
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Input of litter (solid waste matter, including micro-sized litter)
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Coastal ecosystems
|
Coastal ecosystems
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Other pelagic habitats
|
Coastal ecosystems
|
Coastal ecosystems
|
Other pelagic habitats
|
Coastal ecosystems
|
Coastal ecosystems
|
Litter in the environment
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Coastal ecosystems
|
Coastal ecosystems
|
Coastal ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Aquaculture – marine, including infrastructure
|
Fish and shellfish harvesting (professional, recreational)
|
Hunting and collecting for other purposes
|
Marine plant harvesting
|
Extraction of minerals (rock, metal ores, gravel, sand, shell)
|
Extraction of oil and gas, including infrastructure
|
Extraction of water
|
Military operations (subject to Article 2(2))
|
Transmission of electricity and communications (cables)
|
Renewable energy generation (wind, wave and tidal power), including infrastructure
|
Research, survey and educational activities
|
Coastal defence and flood protection
|
Offshore structures (other than for oil/gas/renewables)
|
Restructuring of seabed morphology, including dredging and depositing of materials
|
Tourism and leisure activities
|
Tourism and leisure infrastructure
|
Transport infrastructure
|
Transport – shipping
|
Waste treatment and disposal
|
Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events
|
Input of litter (solid waste matter, including micro-sized litter)
|
Input of nutrients – diffuse sources, point sources, atmospheric deposition
|
Input of anthropogenic sound (impulsive, continuous)
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Input of litter (solid waste matter, including micro-sized litter)
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Coastal ecosystems
|
Coastal ecosystems
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Other pelagic habitats
|
Coastal ecosystems
|
Coastal ecosystems
|
Other pelagic habitats
|
Coastal ecosystems
|
Coastal ecosystems
|
Litter in the environment
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Coastal ecosystems
|
Coastal ecosystems
|
Coastal ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
|
Aquaculture – marine, including infrastructure
|
Fish and shellfish harvesting (professional, recreational)
|
Hunting and collecting for other purposes
|
Marine plant harvesting
|
Extraction of minerals (rock, metal ores, gravel, sand, shell)
|
Extraction of oil and gas, including infrastructure
|
Extraction of water
|
Military operations (subject to Article 2(2))
|
Transmission of electricity and communications (cables)
|
Renewable energy generation (wind, wave and tidal power), including infrastructure
|
Research, survey and educational activities
|
Coastal defence and flood protection
|
Offshore structures (other than for oil/gas/renewables)
|
Restructuring of seabed morphology, including dredging and depositing of materials
|
Tourism and leisure activities
|
Tourism and leisure infrastructure
|
Transport infrastructure
|
Transport – shipping
|
Waste treatment and disposal
|
Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events
|
Input of litter (solid waste matter, including micro-sized litter)
|
Input of nutrients – diffuse sources, point sources, atmospheric deposition
|
Input of anthropogenic sound (impulsive, continuous)
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Input of litter (solid waste matter, including micro-sized litter)
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Coastal ecosystems
|
Coastal ecosystems
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Other pelagic habitats
|
Coastal ecosystems
|
Coastal ecosystems
|
Other pelagic habitats
|
Coastal ecosystems
|
Coastal ecosystems
|
Litter in the environment
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Eutrophication
|
Eutrophication
|
Benthic broad habitats
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
|
Coastal ecosystems
|
Coastal ecosystems
|
Coastal ecosystems
|
Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Established non-indigenous species
|
Newly introduced non-indigenous species
|
Established non-indigenous species
|
|
Aquaculture – marine, including infrastructure
|
Fish and shellfish harvesting (professional, recreational)
|
Hunting and collecting for other purposes
|
Marine plant harvesting
|
Extraction of minerals (rock, metal ores, gravel, sand, shell)
|
Extraction of oil and gas, including infrastructure
|
Extraction of water
|
Military operations (subject to Article 2(2))
|
Transmission of electricity and communications (cables)
|
Renewable energy generation (wind, wave and tidal power), including infrastructure
|
Research, survey and educational activities
|
Coastal defence and flood protection
|
Offshore structures (other than for oil/gas/renewables)
|
Restructuring of seabed morphology, including dredging and depositing of materials
|
Tourism and leisure activities
|
Tourism and leisure infrastructure
|
Transport infrastructure
|
Transport – shipping
|
Waste treatment and disposal
|
Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events
|
Input of litter (solid waste matter, including micro-sized litter)
|
Input of nutrients – diffuse sources, point sources, atmospheric deposition
|
Input of anthropogenic sound (impulsive, continuous)
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Input of litter (solid waste matter, including micro-sized litter)
|
Coastal fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Coastal fish
|
Demersal shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Coastal ecosystems
|
Coastal ecosystems
|
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Pelagic shelf fish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
|
Commercially exploited fish and shellfish
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Other pelagic habitats
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Coastal ecosystems
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Coastal ecosystems
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Other pelagic habitats
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Coastal ecosystems
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Coastal ecosystems
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Litter in the environment
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Input or spread of non-indigenous species
|
Input or spread of non-indigenous species
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Eutrophication
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Eutrophication
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Benthic broad habitats
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Input or spread of non-indigenous species
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Input or spread of non-indigenous species
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Input or spread of non-indigenous species
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Coastal ecosystems
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Coastal ecosystems
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Coastal ecosystems
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Eutrophication
|
Benthic broad habitats
|
Benthic broad habitats
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Newly introduced non-indigenous species
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Established non-indigenous species
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Established non-indigenous species
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Established non-indigenous species
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Newly introduced non-indigenous species
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Established non-indigenous species
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Elements |
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GES criteria |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C3 |
D1C3 |
D1C3 |
D1C3 |
D1C4 |
D1C4 |
D1C4 |
D3C1 |
D3C1 |
D3C2 |
D3C2 |
D3C3 |
D3C3 |
D3C3 |
D3C3 |
D4C1 |
D4C2 |
D1C1 |
D1C2 |
D1C3 |
D3C1 |
D3C2 |
D3C3 |
D1C6 |
D4C1 |
D4C2 |
D1C6 |
D4C1 |
D4C2 |
D10C1 |
D2C1 |
D2C2 |
D5C6 |
D5C7 |
D6C5 |
D2C1 |
D2C2 |
D2C3 |
D4C1 |
D4C2 |
D4C2 |
D5C8 |
D6C4 |
D6C5 |
D2C1 |
D2C2 |
D2C2 |
D2C2 |
D2C1 |
D2C2 |
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Parameters |
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Parameter Other |
Production (tonnes); Area; Nutrient load |
Catch; By-catch |
Number of individuals hunted by species (waterbird |
Amount (kg); Area |
Mining volume; Mining area; Area pressure index |
Pipe length (area); Area pressure index |
Volume |
Number of explosions; Number of trainings; Trainin |
Cable length (area); Area pressure index |
Area; Area pressure index |
Volume of costs on marine researches; Number of re |
Length of defence structure; Coastline pressure in |
Area of structure; Area pressure index |
Soil volume; Extent; Area pressure index |
Number of vacationists; Number of visits; People's |
Number of marinas per coastline; Length of beach |
Area; Volume (goods and passengers); Number of loa |
Number of ships (incl. number of ships complying w |
Areas of dumping sites and volume of dumped materi |
Pollution load (tonnes/year) - Hg, Cd, Cu, Pb, Zn, |
Amount in sediments; Litter type and material |
Pollution load (tonnes/year) - N, P, BHT5 |
Number of disturbance days - Impulsive underwater |
Mass (catch weight per unit effort) |
Abundance index of European eel in monitoring catc |
Mass (catch weight per unit effort) |
Mass (catch weight per unit effort) |
Mass (catch weight per unit effort) |
Mass (catch weight per unit effort) |
Mass (catch weight per unit effort) |
Mass (catch mass per unit effort) |
Mass (catch mass per unit effort) |
Mass (catch mass per unit effort) |
Ratio between annual commercial catch and biomass |
Mass (commercial catch weight per unit effort) |
Age distribution |
Age distribution; Sex distribution |
Mass (commercial catch weight per unit effort) |
Sex distribution; Age distribution |
Species composition; Trophic level class of fish s |
Abundance of coastal fish key functional groups (C |
Age distribution |
Species composition; Abundance (number of individu |
Species composition |
Species composition; Abundance (number of individu |
Species composition |
Abundance (number of individuals); Biomass |
Species composition; Presence; Relative abundance |
Species composition; Presence; Relative abundance |
Species composition; Presence; Relative abundance |
Abundance (number of individuals); Biomass |
Abundance (number of individuals); Biomass |
Species composition |
Extent |
Extent |
Species composition; Biomass |
Species composition; Abundance; Biomass |
Species composition; Abundance (number of individu |
Species composition; Relative biomass in community |
Species composition |
Species composition; Abundance (number of individu |
Species composition |
||||||||||||||||||||
Spatial scope |
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Marine reporting units |
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Temporal scope (start date - end date) |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
2015-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1975-9999 |
1992-9999 |
1992-9999 |
1992-9999 |
1992-9999 |
1992-9999 |
1992-9999 |
1992-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
1993-9999 |
1995-9999 |
1995-9999 |
1995-9999 |
1995-9999 |
1995-9999 |
1995-9999 |
1991-9999 |
1991-9999 |
1991-9999 |
1991-9999 |
1991-9999 |
1991-9999 |
1991-9999 |
1991-9999 |
1991-9999 |
2010-9999 |
2010-9999 |
2010-9999 |
2010-9999 |
2010-9999 |
2010-9999 |
Monitoring frequency |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Other |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Monitoring type |
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Monitoring method |
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Monitoring method other |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
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. |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
ICES WGBFAS |
The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined. |
The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined. |
The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined. |
The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined. |
The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined. |
The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined. |
The monitoring and assessment of the state of herring and sprat stocks are following the ICES WGBFAS methodology. Herring and sprat stocks and stock trends are assessed on the basis of the catches. Based on the collected material, biological analyses are performed and the age of the individuals is determined. |
National monitoring programme |
National monitoring programme |
National monitoring programme |
National monitoring programme |
National monitoring programme |
National monitoring programme |
National monitoring programme |
National monitoring programme |
National monitoring programme |
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf); |
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf); |
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf); |
Joint HELCOM/OSPAR Guidelines on the granting of exemptions under the International Convention for the Control and Management of Ships’ Ballast Water and Sediments, Regulation A (https://www.helcom.fi/wp-content/uploads/2019/08/Joint-HELCOM_OSPAR-Guidelines.pdf); |
The numerical data used are calculated on the basis of data collected under other programmes. The level of biopollution is assessed on the basis of a scientifically validated methodology (Olenin et al. 2007) for an average of three sub-basins (the Gulf of Riga, the Gulf of Finland and the Baltic Proper). |
The numerical data used are calculated on the basis of data collected under other programmes. The level of biopollution is assessed on the basis of a scientifically validated methodology (Olenin et al. 2007) for an average of three sub-basins (the Gulf of Riga, the Gulf of Finland and the Baltic Proper). |
||||||||||||
Quality control |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
Data quality control systems of relevant data sources. |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
General requirements for the competence of testing and calibration laboratories are filled according to ISO/IEC 17025 and the recommendations of monitoring manuals are followed (HELCOM, ICES WGBFAS). |
ICES WGBFAS
|
ICES WGBFAS
|
ICES WGBFAS
|
ICES WGBFAS
|
ICES WGBFAS
|
ICES WGBFAS
|
ICES WGBFAS
|
The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed. |
The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed. |
The quality is ensured by following the standard methods and HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed. |
The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed. |
The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed. |
The quality is ensured by following the HELCOM guidance as well as accreditation of experts and persons by whom the monitoring is performed. |
The quality is ensured by following the HELCOM guidances recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the HELCOM guidances recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the HELCOM guidances recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the HELCOM guidances recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the HELCOM guidances recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the HELCOM guidances recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by following the OSPAR/HELCOM guidance (OSPAR JAMP Eutrophication Monitoring Guidelines: Benthos (Agreement 2012-12) (Replaces Agreement 1997-06) recommendations, accreditation of experts and persons by whom the monitoring is performed and filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025. |
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations. |
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations. |
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations. |
The quality is ensured by the accreditation of experts and persons by whom the monitoring is performed and following guidance recommendations. |
The monitoring and assessment quality is assured by regional coordination via HELCOM, following the HELCOM, HELCOM/OSPAR and national monitoring guidelines, and accreditation of experts and persons by whom the monitoring is performed. |
The monitoring and assessment quality is assured by regional coordination via HELCOM, following the HELCOM, HELCOM/OSPAR and national monitoring guidelines, and accreditation of experts and persons by whom the monitoring is performed. |
Data management |
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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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 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. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are reported annually to the Ministry of the Environment and the Ministry of Rural Affairs. The raw data are also stored in databases of Estonian Marine Institute at Tartu University. |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Gathered data are reported to the national environmental monitoring database KESE. |
Gathered data are reported to the national environmental monitoring database KESE. |
Gathered data are reported to the national environmental monitoring database KESE. |
Gathered data are reported to the national environmental monitoring database KESE. |
Gathered data are reported to the national environmental monitoring database KESE. |
Gathered data are reported to the national environmental monitoring database KESE. |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March). |
Data are yearly reported to the national environmental monitoring database KESE (by 1 March). |
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). |
The data are yearly reported to the national environmental monitoring database KESE (by 1 March). |
Data access |
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Contact |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.ee. |
Ministry of the Environment: Elo Rasmann (elo.rasmann@envir.ee);
University of Tartu, Estonian Marine Institute: Redik Eschbaum, redik.eschbaum@ut.ee, Lauri Saks, lauri.saks@ut.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 |
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 |
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 |
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 |
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 |
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 |
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 |
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References |
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). |
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). |
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). |
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). |
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). |
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). |
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). |
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). |
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). |
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). |
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). |
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). |