As part of EEA's ongoing security and identity management improvements, we are currently migrating the system to Entra ID authentication.
We kindly ask all users to start using Entra ID credentials when logging in to the system. 

Please note that LDAP authentication will be phased out and disabled by the end of August 2026. We encourage you to verify that you can successfully access the system and that your account and permissions function as expected after Entra ID login. Should you encounter any issues or require assistance during this transition, please contact Laszlo Cseh at laszlo.cseh@eaudeweb.ro Thank you for your cooperation and support.
As part of EEA's ongoing security and identity management improvements, we are currently migrating the system to Entra ID authentication.
We kindly ask all users to start using Entra ID credentials when logging in to the system. 

Please note that LDAP authentication will be phased out and disabled by the end of August 2026. We encourage you to verify that you can successfully access the system and that your account and permissions function as expected after Entra ID login. Should you encounter any issues or require assistance during this transition, please contact Laszlo Cseh at laszlo.cseh@eaudeweb.ro Thank you for your cooperation and support.

Member State report / Art11 / 2014-2020 / D2 / Netherlands / NE Atlantic: Greater North 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 Netherlands
Region/subregion NE Atlantic: Greater North Sea
Reported by Rijkswaterstaat
Report date 2014-10-16; 2020-11-17
Report access
2014 data
2020 data
Monitoring programme Monitoring programme name
Monitoring programme Reference existing programme
Monitoring programme Marine Unit ID
Q4e - Programme ID
Q4f - Programme description
Q5e - Natural variability
Q5d - Adequacy for assessment of GES Q5d - Adequate data
Q5d - Adequacy for assessment of GES Q5d - Established methods
Q5d - Adequacy for assessment of GES Q5d - Adequate understanding of GES
Q5d - Adequacy for assessment of GES Q5d - Adequate capacity
Q5f - Description of programme for GES assessment
Q5g - Gap-filling date for GES assessment
Q5h - Plans to implement monitoring for GES assessment
Q6a -Relevant targets Q6a - Environmental target
Q6a -Relevant targets Q6a - Associated indicator
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Q6b - Adequacy for assessment of targets Q6b_EstablishedMethods
Q6b - Adequacy for assessment of targets Q6d_AdequateCapacity
Q6c - Target updating
Q6d - Description of programme for targets assessment
Q6e - Gap-filling date for targets assessment
Q6f - Plans to implement monitoring for targets assessment
Q7a - Relevant activities
Q7b - Description of monitoring of activities
Q7c - Relevant measures
Q7e - Adequacy for assessment of measures Q7d - Adequate data
Q7e - Adequacy for assessment of measures Q7d - Established methods
Q7e - Adequacy for assessment of measures Q7d - Adequate understanding of GES
Q7e - Adequacy for assessment of measures Q7d - Adequate capacity
Q7e - Adequacy for assessment of measures Q7d - Addresses activities and pressures
Q7e - Adequacy for assessment of measures Q7d - Addresses effectiveness of measures
Q7d - Description of monitoring for measures
Q7f - Gap-filling date for activities and measures
Q8a - Links to existing Monitoring Programmes
Reference sub-programme Sub-programme ID
Reference sub-programme Sub-programme name
Q4g - Sub-programmes Sub-programme ID
Q4g - Sub-programmes Sub-programme name
Q4k - Monitoring purpose
Q4l - Links of monitoring programmes of other Directives and Conventions
Q5c - Features Q5c - Habitats
Q5c - Features Q5c - Species list
Q5c - Features Q5c - Physical/Chemical features
Q5c - Features Q5c - Pressures
Q9a - Elements
Q5a - GES criteria Relevant GES criteria
Q5b - GES indicators Relevant GES indicators
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
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
Descriptor
D2
Monitoring strategy description
The principal purpose of the MSFD monitoring programme is to review the progress that has been made towards achieving good environmental status prescribed for each criterion in the Marine Strategy Part I (2018). This review is based on established indicators. The monitoring can also be used to evaluate the environmental targets defined for each descriptor. The environmental targets are operational in nature and are linked to specific actions and/or measures in the Marine Strategy Part 3. The effects of individual measures cannot generally be linked directly to environmental status or the criteria. Monitoring data can, however, indirectly give an indication of the effectiveness of measures. The monitoring (methods, spatial and temporal coverage) aims to achieve sufficient statistical confidence in the assessment. The risk of not achieving GES or deterioration from GES is addressed in the Marine Strategy, Parts 1 and 3. The European Commission requests that the electronic reports explain how the DPSIR cycle is monitored and to which part of the cycle the monitoring surveys are linked. The MSFD monitoring programme helps to generate better insight into the relationships between the use of the sea and the marine ecosystem. This can be accomplished by monitoring pressures and the underlying activities (D1C1: incidental bycatch, D2: non-indigenous species, D3C1: fish mortality, D5: eutrophication, D6C1/D6C4: physical loss of seabed/habitats and D6C2: fisheries intensity and sand extraction, D8 and D9: pollutants, D10: litter, D11: underwater noise), and by monitoring species and habitats (D1: biodiversity (with the exception of D1C1), D3C2: spawning stock biomass, D4: food web, D6C3/D6C5: habitats ) and hydrographical characteristics (D7). The numerous relationships between the various elements of the marine ecosystem are complex, and many are still not known. Consequently, it is often only possible to give an indication of the impact of specific activities on the marine ecosystem. Experts generally derive DPSIR relationships from the monitoring of pressures/activities and of species and habitats (from the MSFD monitoring programme), in combination with data derived from permits and research programmes. However, some surveys have been established to measure pressures and their effects and/or to learn more about the effectiveness of measures. In designing the monitoring survey for benthic animals (habitats), the Netherlands explicitly took account of the need to
Coverage of GES criteria
Adequate monitoring was in place in 2014
Gaps and plans
The Netherlands takes a pragmatic approach, whereby there are no monitoring surveys specifically set up for D2 and the assessment is based on data collected for other purposes. Hence, strictly spoken, there are no gaps in the MSFD monitoring programme. Because all available observations are used for the assessment, the full scale of the monitoring effort is not known. As a result, firm quantitative judgements of the introduction rates of non-indigenous marine species might be more difficult to substantiate.
Related targets
  • ANSNL-D2T1
Coverage of targets
Adequate monitoring was in place in 2014
Related measures
  • ANSNL-M006 - 'Voorwaarden aan vergunningverlening ter voorkoming van de verspreiding van niet-inheemse soorten'
  • ANSNL-M007 - 'Beheer Natura 2000-gebieden (niet-inheemse soorten)'
  • ANSNL-M042 - 'Verordening preventie en beheer invasieve soorten'
  • ANSNL-M043 - 'Tegengaan verspreiding soorten via ballastwater'
  • ANSNL-M044 - 'Uitvoering protocollen voor vrijstellingen na inwerkingtreding Ballastwaterconventie'
  • ANSNL-M045 - 'Uitvoering van Hull Fouling Guidelines tegen aangroei niet-inheemse soorten op scheepshuiden'
Coverage of measures
Adequate monitoring was in place in 2014
Related monitoring programmes
  • ANSNL-D02-Sub1
Programme code
ANSNL-D02-Sub1
Programme name
Non-indigenous species - from specific sources
Update type
Modified from 2014
Old programme codes
Programme description
Monitoring must provide insight into the number of non-indigenous species that are introduced into the Dutch section of the North Sea in each six-year planning period. To establish the effectiveness of regulatory and other measures, it is important to ascertain the route by which these species have been introduced (the pathway approach). In view of the small chance of their discovery at the introduction stage and the lack of options for intervention if non-indigenous species are discovered, the Netherlands currently opts for assessment on the basis of the best available knowledge. All observations of non-indigenous marine species in the Dutch North Sea are considered together, including those from sources other than regular monitoring surveys. The regular monitoring surveys include the biological measurements by Rijkswaterstaat (MWTL: macrozoobenthos and phytoplankton) and for the Ministry of Agriculture, Nature and Food Quality (WOT: macrozoobenthos and fish). An additional feature compared with 2014 is the additional use of project-based monitoring (construction of wind farms, impact of beach nourishment) and well-documented observations by the public (divers and beach working groups of the Dutch Natural History Society (KNNV), for example). The MWTL benthos monitoring is carried out once every three years; the monitoring of phytoplankton is conducted annually, as are the WOT-Shellfish and CFP-Fisheries monitoring. For further details, see D6 (macrozoobenthos), D1C6 (phytoplankton) and D3 (fish). The MSFD monitoring is linked to developments in OSPAR and any changes that ensue from the European Regulation on the prevention and management of the introduction and spread of invasive alien species (EU 1143/2014) and the Ballast Water Management Convention (2017).
Monitoring purpose
  • Effectiveness of measures
  • Pressures in the marine environment
Other policies and conventions
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
Regional cooperation - coordinating body
  • OSPAR
Regional cooperation - countries involved
NL
Regional cooperation - implementation level
Agreed data collection methods
Monitoring details
The MWTL (benthos and phytoplankton), the Statutory Research Tasks (SRT) for shellfish and the monitoring of fisheries for the Common Fisheries Policy (CFP) are the regular monitoring surveys used to detect non-indigenous species in the Dutch section of the North Sea. Project-based monitoring (construction of wind farms, impact of beach nourishment) and well-documented observations by the public (divers and beach working groups of the Dutch Natural History Society (KNNV), for example) are also used. The MWTL benthos monitoring is carried out once every three years; the monitoring of phytoplankton is conducted annually, as are the SRT-Shellfish and CFP-Fisheries monitoring.
Features
Newly introduced non-indigenous species
Newly introduced non-indigenous species
Newly introduced non-indigenous species
Newly introduced non-indigenous species
Elements
  • Not Applicable
GES criteria
D2C1
Parameters
  • Incidence
Parameter Other
Spatial scope
  • EEZ (or similar)
Marine reporting units
  • ANS-NL-MS-1
  • L1.2
Temporal scope (start date - end date)
2014-9999
Monitoring frequency
Other
Monitoring type
  • In-situ sampling coastal
  • In-situ sampling offshore
Monitoring method
  • OSPAR CEMP Guideline: Common Indicator - Changes to non-indigenous species communities (NIS3) (Agreement 2018-04)
  • Other monitoring method
Monitoring method other
All observations of non-indigenous marine species in the Dutch North Sea are considered together, including those from sources other than regular monitoring surveys. The regular monitoring surveys include the biological measurements by Rijkswaterstaat (MWTL: benthos and phytoplankton) and for the Ministry of Agriculture, Nature and Food Quality (WOT: benthos and fish). An additional feature compared with 2014 is the additional use of monitoring of specific projects (construction of wind farms, effects of beach nourishment) and of well-documented observations by members of the public (including divers). The MSFD monitoring is linked to developments in OSPAR and any changes that ensue from the European Regulation on the prevention and management of the introduction and spread of invasive alien species (2014) and the Ballast Water Management Convention (2017).
Quality control
Every six years, the Netherlands assesses the rate of introduction of non-native species based on the best available knowledge. All available observations of non-native marine species (including from regular monitoring) are considered together (GIMARES,2017). All available data are assessed using a method developed by GiMaRIS. GiMaRIS uses ISO 9001 certified working methods. Reference: https://www.noordzeeloket.nl/publish/pages/138273/non-indigenous_marine_species_in_the_netherlands.pdf
Data management
Marine Information and Data Centre
Data access
Related indicator/name
  • ANSNL-OSPAR-D2C1-exoten2017
Contact
https://www.informatiehuismarien.nl/uk/secundaire-navigatie/contact/
References