Member State report / Art11 / 2014 / D10 / 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
GES Descriptor D10 Litter
Member State Netherlands
Region/subregion NE Atlantic: Greater North Sea
Reported by Rijkswaterstaat
Report date 2014-10-16
Report access
Monitoring programme Monitoring programme name
MP_D10
MP_D10
Monitoring programme Reference existing programme
Monitoring programme Marine Unit ID
Q4e - Programme ID
ANSNL-D10
ANSNL-D10
Q4f - Programme description
The Cabinet views this MSFD Monitoring Programme as a guiding component of the approach to ensure a good status of the marine environment in the Dutch part of the North Sea. The MSFD Monitoring Programme has been drawn up in accordance with Article 11 of the Directive. It details the actual monitoring of the 32 indicators outlined in the Marine Strategy Part 1. Based on the measurement data, the Monitoring Programme provides insight into: 1. The status of the indicators, thereby indicating the extent to which an environmental target is achieved (MSFD, Art. 10), in order to facilitate the ongoing assessment and periodic updating of the environmental targets (MSFD, Art. 5) in order to maintain or reach good environmental status. 2. The effectiveness of the programme of measures to be implemented under the MSFD. Although the Monitoring Programme focuses primarily on the 32 indicators from the Marine Strategy Part 1, it also uses, for the purpose of interpreting the results, a number of supporting parameters that are included as standard during sampling (such as temperature, acidity, conductivity, salinity and dissolved oxygen). For the purpose of the next assessment of the environmental status in 2017-2018 and assessments thereafter, use will also be made of the information resulting from monitoring for research or from other statutory frameworks and policy areas. This includes information from national monitoring under the Bathing Water Directive in the area of microbial pathogens, shipping intensity monitoring (including fishing vessels) for the purpose of shipping traffic safety and bathymetric information obtained from hydrographic measurements. In determing spatial and temporal distribution of the monitoring, natural variation is taken into account as well as the possibilities to distinguish changes from natural variability. Important parameters for climate change and ocean acidification, such as temperature and pH are incorporated in the regular monitoring programmes. Economic data is collected by Statistics Netherlands (abbreviated as CBS in Dutch). CBS supplies the required data following receipt of a specified request for information. Thus, the requirements of MSFD Art. 8 are met and the indicative list of elements included in MSFD Appendix III is incorporated. In this way, the MSFD Monitoring Programme provides a solid basis for updating the Marine Strategy during the second implementation cycle of the MSFD. This begins by updating the initial assessment (MSFD Art. 8) and describing the good environmental status (MSFD Art. 9), environmental targets and indicators (MSFD Art. 10) in 2018, and continues through to the adjustment of the existing programme of measures (Art. 13) in 2021. References: -More information on the rationale for the balance between monitoring of state/impact, pressures, activities and measures: MS II paragraph 2.3 (DPSIR –model) -MS II Annex 4
The Cabinet views this MSFD Monitoring Programme as a guiding component of the approach to ensure a good status of the marine environment in the Dutch part of the North Sea. The MSFD Monitoring Programme has been drawn up in accordance with Article 11 of the Directive. It details the actual monitoring of the 32 indicators outlined in the Marine Strategy Part 1. Based on the measurement data, the Monitoring Programme provides insight into: 1. The status of the indicators, thereby indicating the extent to which an environmental target is achieved (MSFD, Art. 10), in order to facilitate the ongoing assessment and periodic updating of the environmental targets (MSFD, Art. 5) in order to maintain or reach good environmental status. 2. The effectiveness of the programme of measures to be implemented under the MSFD. Although the Monitoring Programme focuses primarily on the 32 indicators from the Marine Strategy Part 1, it also uses, for the purpose of interpreting the results, a number of supporting parameters that are included as standard during sampling (such as temperature, acidity, conductivity, salinity and dissolved oxygen). For the purpose of the next assessment of the environmental status in 2017-2018 and assessments thereafter, use will also be made of the information resulting from monitoring for research or from other statutory frameworks and policy areas. This includes information from national monitoring under the Bathing Water Directive in the area of microbial pathogens, shipping intensity monitoring (including fishing vessels) for the purpose of shipping traffic safety and bathymetric information obtained from hydrographic measurements. In determing spatial and temporal distribution of the monitoring, natural variation is taken into account as well as the possibilities to distinguish changes from natural variability. Important parameters for climate change and ocean acidification, such as temperature and pH are incorporated in the regular monitoring programmes. Economic data is collected by Statistics Netherlands (abbreviated as CBS in Dutch). CBS supplies the required data following receipt of a specified request for information. Thus, the requirements of MSFD Art. 8 are met and the indicative list of elements included in MSFD Appendix III is incorporated. In this way, the MSFD Monitoring Programme provides a solid basis for updating the Marine Strategy during the second implementation cycle of the MSFD. This begins by updating the initial assessment (MSFD Art. 8) and describing the good environmental status (MSFD Art. 9), environmental targets and indicators (MSFD Art. 10) in 2018, and continues through to the adjustment of the existing programme of measures (Art. 13) in 2021. References: -More information on the rationale for the balance between monitoring of state/impact, pressures, activities and measures: MS II paragraph 2.3 (DPSIR –model) -MS II Annex 4
Q5e - Natural variability
  • Other
  • not applicable: litter does not belong in the marine environment and is purely anthropogenic
  • Other
  • not applicable: litter does not belong in the marine environment and is purely anthropogenic
Q5d - Adequacy for assessment of GES Q5d - Adequate data
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Established methods
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate understanding of GES
Y
Y
Q5d - Adequacy for assessment of GES Q5d - Adequate capacity
Y
Y
Q5f - Description of programme for GES assessment
a,b,c) In the art 9 and 10 report in 2012 the Netherlands has opted for a general description of GES under art 9 and a further elaboration of the targets and associated indicators under art 10. These targets and indicators cover all criteria from the Commission Decision as far as they are considered relevant for the Netherlands part of the North Sea. Therefore, they also cover the information requirement for the assessment of the descriptors and targets. See paragraph 9.2.12 of the Marine Strategy II for a detailed description of how the targets and the information required to describe GES, via the elaboration of an information strategy, functional requirements and a monitoring strategy, are translated into the monitoring plan. Changes in the amount of suspended and floating litter are being monitored by beach litter surveys and counts of plastic particles in the stomachs of fulmars. Litter on the seabed is being monitored in conjunction with the IBTS fish monitoring programme. When the OSPAR common indicator on seabed litter will become operational (expected in 2015 or 2016) this will be taken up in the monitoring programme as a new sub-programme. At present, there are no standard methodologies for the monitoring of micro- and nano-plastics. Experimental and field research will contribute to the development of indicators for these small plastic particles. d) the amount of litter on the beach is being influenced by the direction and force of the wind in the period before the monitoring takes place. Effects of changes in anthropogenic pressure can be distinguished from fluctuations due to weather conditions by a trend-analysis of long-term monitoring series. e) The MSFD Monitoring Plan will be updated annually in a digitally amended supplement based on the latest developments and insights in the area of indicator definitions and measurement methods, for example as a result from (sub) regional coordination within OSPAR.
a,b,c) In the art 9 and 10 report in 2012 the Netherlands has opted for a general description of GES under art 9 and a further elaboration of the targets and associated indicators under art 10. These targets and indicators cover all criteria from the Commission Decision as far as they are considered relevant for the Netherlands part of the North Sea. Therefore, they also cover the information requirement for the assessment of the descriptors and targets. See paragraph 9.2.12 of the Marine Strategy II for a detailed description of how the targets and the information required to describe GES, via the elaboration of an information strategy, functional requirements and a monitoring strategy, are translated into the monitoring plan. Changes in the amount of suspended and floating litter are being monitored by beach litter surveys and counts of plastic particles in the stomachs of fulmars. Litter on the seabed is being monitored in conjunction with the IBTS fish monitoring programme. When the OSPAR common indicator on seabed litter will become operational (expected in 2015 or 2016) this will be taken up in the monitoring programme as a new sub-programme. At present, there are no standard methodologies for the monitoring of micro- and nano-plastics. Experimental and field research will contribute to the development of indicators for these small plastic particles. d) the amount of litter on the beach is being influenced by the direction and force of the wind in the period before the monitoring takes place. Effects of changes in anthropogenic pressure can be distinguished from fluctuations due to weather conditions by a trend-analysis of long-term monitoring series. e) The MSFD Monitoring Plan will be updated annually in a digitally amended supplement based on the latest developments and insights in the area of indicator definitions and measurement methods, for example as a result from (sub) regional coordination within OSPAR.
Q5g - Gap-filling date for GES assessment
By2014
By2014
Q5h - Plans to implement monitoring for GES assessment
The internationally coordinated indicators (31) litter on beaches and (32) plastic in stomachs of northern fulmars are already being used in the North Sea region in the context of OSPAR. In 2013, the OSPAR commission designated litter on the seabed as a prioritised candidate indicator. This indicator can be established as a common indicator in one to two years. The indicator IBTS (International Bottom Trawl Survey) is being developed for this. In anticipation of this, Rijkswaterstaat is already carrying out this study in combination with ICES fish monitoring. If necessary and depending on when this process will yield results, the MSFD Monitoring Plan will be adjusted in 2015 or 2016. In cooperation with the International River commissions the sources of litter are being looked into, in particular from litter that enters the marine environment through the rivers. Experimental and field research contributes to the development of an indicator for microplastics in OSPAR, including a risk assessment for organisms. Risks of nanoplastics are also being mapped. The indicators mentioned above, such as litter on beaches and on the seabed and plastic particles in stomach of fulmars, and the results of the research will contribute to the OSPAR Intermediate Assessment in 2017 and the OSPAR QSR 2021
The internationally coordinated indicators (31) litter on beaches and (32) plastic in stomachs of northern fulmars are already being used in the North Sea region in the context of OSPAR. In 2013, the OSPAR commission designated litter on the seabed as a prioritised candidate indicator. This indicator can be established as a common indicator in one to two years. The indicator IBTS (International Bottom Trawl Survey) is being developed for this. In anticipation of this, Rijkswaterstaat is already carrying out this study in combination with ICES fish monitoring. If necessary and depending on when this process will yield results, the MSFD Monitoring Plan will be adjusted in 2015 or 2016. In cooperation with the International River commissions the sources of litter are being looked into, in particular from litter that enters the marine environment through the rivers. Experimental and field research contributes to the development of an indicator for microplastics in OSPAR, including a risk assessment for organisms. Risks of nanoplastics are also being mapped. The indicators mentioned above, such as litter on beaches and on the seabed and plastic particles in stomach of fulmars, and the results of the research will contribute to the OSPAR Intermediate Assessment in 2017 and the OSPAR QSR 2021
Q6a -Relevant targets Q6a - Environmental target
10a 10b
10a 10b
Q6a -Relevant targets Q6a - Associated indicator
10a 10b
10a 10b
Q6b - Adequacy for assessment of targets Q6b_SuitableData
Y
Y
Q6b - Adequacy for assessment of targets Q6b_EstablishedMethods
Y
Y
Q6b - Adequacy for assessment of targets Q6d_AdequateCapacity
Y
Y
Q6c - Target updating
Y
Y
Q6d - Description of programme for targets assessment
See 5f
See 5f
Q6e - Gap-filling date for targets assessment
By2014
By2014
Q6f - Plans to implement monitoring for targets assessment
Q7a - Relevant activities
  • Fisheries
  • Industry
  • Shipping
  • TourismRecreation
  • Urban
  • Fisheries
  • Industry
  • Shipping
  • TourismRecreation
  • Urban
Q7b - Description of monitoring of activities
Annex 4 of the Marine Strategy part 2 shows the DPSIR relations between ecosystem elements/descriptors, pressures and activities, as well as how the pressures and activities and their effects are monitored. Annex 3 of the Marine Strategy part 2 gives the relation between elements from the MSFD Annex 3 and the MSFD monitoring programme.
Annex 4 of the Marine Strategy part 2 shows the DPSIR relations between ecosystem elements/descriptors, pressures and activities, as well as how the pressures and activities and their effects are monitored. Annex 3 of the Marine Strategy part 2 gives the relation between elements from the MSFD Annex 3 and the MSFD monitoring programme.
Q7c - Relevant measures
Q7e - Adequacy for assessment of measures Q7d - Adequate data
Y
Y
Q7e - Adequacy for assessment of measures Q7d - Established methods
Q7e - Adequacy for assessment of measures Q7d - Adequate understanding of GES
Y
Y
Q7e - Adequacy for assessment of measures Q7d - Adequate capacity
Y
Y
Q7e - Adequacy for assessment of measures Q7d - Addresses activities and pressures
Y
Y
Q7e - Adequacy for assessment of measures Q7d - Addresses effectiveness of measures
Y
Y
Q7d - Description of monitoring for measures
The monitoring programme renders quantitative information on the amount of litter in the Netherlands part of the Greater North Sea. This information gives insight in the effectiveness of current and future measures. However, absolute source identification remains challenging.
The monitoring programme renders quantitative information on the amount of litter in the Netherlands part of the Greater North Sea. This information gives insight in the effectiveness of current and future measures. However, absolute source identification remains challenging.
Q7f - Gap-filling date for activities and measures
By2014
By2014
Q8a - Links to existing Monitoring Programmes
  • OSPAR
  • OSPAR
Reference sub-programme Sub-programme ID
ANSNL-D10-Sub1-OSPAR-Beach
ANSNL-D10-Sub2-OSPAR-Fulmar
Reference sub-programme Sub-programme name
Litter - characteristics and abundance/volume
Litter - characteristics and abundance/volume
Q4g - Sub-programmes Sub-programme ID
ANSNL-D10-Sub1-OSPAR-Beach
ANSNL-D10-Sub2-OSPAR-Fulmar
Q4g - Sub-programmes Sub-programme name
Litter - characteristics and abundance/volume
Litter - characteristics and abundance/volume
Q4k - Monitoring purpose
Pressurse Measures
StateImpact Pressurse Measures
Q4l - Links of monitoring programmes of other Directives and Conventions
OSPAR Convention for the Protection of the Marine Environment of the North-East Atlantic (OSPAR convention) Name of other programme: OSPAR pre-CEMP Appendix 15 - 'Beach Litter' http://www.ospar.org/documents/dbase/decrecs/agreements/10-01e_the%20cemp.doc
OSPAR Convention for the Protection of the Marine Environment of the North-East Atlantic (OSPAR Convention) Handbook for the application of Ecological Quality Objectives in the North Sea. Second Edition - 2009. OSPAR Biodiversity Series Publication 307/2009
Q5c - Features Q5c - Habitats
  • SeabedHabitatsAll WaterColumnHabitatsAll
  • SeabedHabitatsAll WaterColumnHabitatsAll
Q5c - Features Q5c - Species list
  • BirdsAll
  • BirdsAll
Q5c - Features Q5c - Physical/Chemical features
Q5c - Features Q5c - Pressures
  • Litter
  • Litter
Q9a - Elements
  • Pressure: Other Physical Disturbance: Beach Litter
  • Pressure: Other Physical Disturbance
  • plastic particles and other material in the stomach samples beach-washed fulmars
Q5a - GES criteria Relevant GES criteria
  • 10.1
  • 10.2
  • 10.1
  • 10.2
Q5b - GES indicators Relevant GES indicators
  • 10.1.1
  • 10.1.2
  • 10.2.1
  • 10.1.1
  • 10.1.2
  • 10.2.1
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
  • MP-9b-2-2-1
  • MP-9b-2-2-7
  • MP-9b-2-2-9
Q9b - Parameters monitored (activity) Activity
Q9b Parameters monitored (other) Other
Q41 Spatial scope
WFD_CW TerritorialWaters EEZ
WFD_CW TerritorialWaters EEZ
Q4j - Description of spatial scope
Survey sites are present in the whole north-east Atlantic region. However for OSPAR Beach Litter Monitoring the Bay of Biscay and Iberian coast has been split into two regions and the Greater North Sea has been divided into "Southern North Sea" and "Northern North Sea". This is to reflect the different types and abundances of litter found in these regions. In the Netherlands 4 beaches are surveyed since 2001.
The programme covers the greater North Sea as it was originally developped as part of the OSPAR suite of North Sea Ecological Quality Objectives (EcoQO's) and this area fits within the Fulmar's natural range. In the Netherlands the programme has been running since 1979.
Marine Unit IDs
  • ANSNL
  • ANSNL
Q4h - Temporal scope Start date- End date
2001-9999
2002-9999
Q9h - Temporal resolution of sampling
  • 3monthly
  • Continually
Q9c - Monitoring method
Guideline for monitoring marine litter on the beaches in the OSPAR maritime area (OSPAR agreement 2010-02)
Handbook for the application of Ecological Quality Objectives in the North Sea. Second Edition - 2009. OSPAR Biodiversity Series Publication 307/2009
Q9d - Description of alteration to method
Q9e - Quality assurance
  • Other
  • Quality assurance is outlined in Guideline for monitoring marine litter on the beaches in the OSPAR maritime area (OSPAR agreement 2010-02)
  • Other
  • Quality assurance is outlined in Handbook for the application of Ecological Quality Objectives in the North Sea. Second Edition - 2009. OSPAR Biodiversity Series Publication 307/2009
Q9f - Quality control
OtherQC
OtherQC
Q9g - Spatial resolution of sampling Q9g - Proportion of area covered %
Q9g - Spatial resolution of sampling Q9g - No. of samples
Presently (2013) there are 50 sites in 11 countries along the NE Atlantic coastline. In the Netherlands 4 beaches are monitored.
the monitoring system is based on specimens of Northern Fulmars found dead on beaches or accidentally killed by collisions or fisheries. these are collected continuously on an opportunity basis. Most specimens are provided in cooperation with groups that conduct regular Beached Bird Surveys, but material is also provided through municipal beach cleaning programs or fisheries programs.
Q9i - Description of sample representivity
Q10a - Scale for aggregation of data
  • Region
  • Subregion
  • Subregion
Q10b - Other scale for aggregation of data
Data can also be aggregated at a beach, national, monitoring region, sub region or regional level.
Data can also be aggregated at a national, monitoring region, or sub-regional level (North Sea).
Q10c - Access to monitoring data Q10c - Data type
ProcessedData DataProducts
ProcessedData DataProducts
Q10c - Access to monitoring data Q10c - Data access mechanism
LocationInternationalDC
LocationInternationalDC
Q10c - Access to monitoring data Q10c - Data access rights
Open
Open
Q10c - Access to monitoring data Q10c - INSPIRE standard
EnvMonitoringFacilities
EnvMonitoringFacilities
Q10c - Access to monitoring data Q10c Date data are available
2014-12
2014-12
Q10c - Access to monitoring data Q10c - Data update frequency
Yearly
Yearly
Q10d - Description of data access
Raw data and assessment products will be made available through the OSPAR website. Data will be available at http://www.ospar.org/content/content.asp?menu=01511400000000_000000_000000. Each year in December a basic MSFD-datafile will be made available via the website of the Informatiehuis Marien (http://www.informatiehuismarien.nl/)
Access of data included in ICES DOME is already in place for EC/EEA. Previous raw data can be accessed on request from the contact at IMARES. Future raw data will be available from the OSPAR website. Assessment products are available from the OSPAR website. Data will be available at http://bit.ly/1ggNS2E