Member State report / Art11 / 2014-2020 / D8 / Denmark / 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 | D8 Contaminants |
| Member State | Denmark |
| Region/subregion | NE Atlantic: Greater North Sea |
| Reported by | Danish Nature Agency |
| Report date | 2014-10-15; 2020-10-19 |
| Report access |
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/ansdk/envvdus4a/ANSDK-D06-04_abundance_softbottomfauna.xml
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/ansdk/envvdus4a/ANSDK-D06-03_abundance_softbottomflora.xml
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/ansdk/envvduppa/ANSDK-D03-05_mortal_fisheries_porpoise.xml
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/ansdk/envvdukzg/ANSDK-D01-18_habitats_mammals_porpoise.xml
http://cdr.eionet.europa.eu/dk/eu/msfd_mp/ansdk/envvdukzg/ANSDK-D01-02_abundance_birds_wintering.xml
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2014 data
2020 data
| Monitoring programme | Monitoring programme name | MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
MP_D8 |
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| Monitoring programme | Reference existing programme | |||||||||||||||
| Monitoring programme | Marine Unit ID |
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| Q4e - Programme ID | ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
ANSDK-D08 |
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| Q4f - Programme description | The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
The programme consists of a number of subprogrammes that reflects the main concept of the DPSIR causal framework. |
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| Q5e - Natural variability |
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| Q5d - Adequacy for assessment of GES | Q5d - Adequate data | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q5d - Adequacy for assessment of GES | Q5d - Established methods | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q5d - Adequacy for assessment of GES | Q5d - Adequate understanding of GES | N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
N |
| Q5d - Adequacy for assessment of GES | Q5d - Adequate capacity | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q5f - Description of programme for GES assessment | The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
The programme provides answers to assessing the monitored vaues of the selected indicators in relation to Community legislation |
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| Q5g - Gap-filling date for GES assessment | By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
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| Q5h - Plans to implement monitoring for GES assessment | Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
Monitoring programme under establishemnt in the Danish parts of the North Sea and Skagerrak in 2015 and onwards. However, monitoring is ongoing in the Kattegat area which is a part of the subregion North Sea. |
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| Q6a -Relevant targets | Q6a - Environmental target | DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
DK_15_ANS DK_26_ANS DK_38_ANS |
| Q6a -Relevant targets | Q6a - Associated indicator | DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
DK_15_ANS DK_38_ANS |
| Q6b - Adequacy for assessment of targets | Q6b_SuitableData | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q6b - Adequacy for assessment of targets | Q6b_EstablishedMethods | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q6b - Adequacy for assessment of targets | Q6d_AdequateCapacity | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
| Q6c - Target updating | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
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| Q6d - Description of programme for targets assessment | The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 8. together with existing data series information on variability, trends and levels recorded earlier will render data for assessing possible progress towards reaching targets. |
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| Q6e - Gap-filling date for targets assessment | By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
By2018 |
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| Q6f - Plans to implement monitoring for targets assessment | ||||||||||||||||
| Q7a - Relevant activities |
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| Q7b - Description of monitoring of activities | The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
The D08 programme records aspects related to spatial distribution of contaminants in the envirtonment, intensity and frequency of acitivity leading to inputs of contaminants. |
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| 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 | By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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| Q8a - Links to existing Monitoring Programmes |
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| Reference sub-programme | Sub-programme ID | ANSDK-D08-01_health_birds_breeding |
ANSDK-D08-02_health_fish_demersal |
ANSDK-D08-03_health_fish_commercial |
ANSDK-D08-04_health_fish_sandeel |
ANSDK-D08-06_health_fish_coastal |
ANSDK-D08-07_health_fish_migratory |
ANSDK-D08-08_health_fish_migratory_pelagic |
ANSDK-D08-09_mortality_birds |
ANSDK-D08-10_health_hardbottomfauna |
ANSDK-D08-12_health_softbottomfauna |
ANSDK-D08-13_CONTAMIN_input_atmos |
ANSDK-D08-14_CONTAMIN_INPUT_point_sources |
ANSDK-D08-17_CONTAMINAN_water |
ANSDK-D08-18_CONTAMINAN_sediment |
ANSDK-D08-19_CONTAMINAN_species |
| Reference sub-programme | Sub-programme name | Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Benthic species - health status |
Benthic species - health status |
Contaminant inputs - from atmosphere |
Contaminant inputs - land-based sources |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Contaminant levels - in species, including seafood |
| Q4g - Sub-programmes | Sub-programme ID | ANSDK-D08-01_health_birds_breeding |
ANSDK-D08-02_health_fish_demersal |
ANSDK-D08-03_health_fish_commercial |
ANSDK-D08-04_health_fish_sandeel |
ANSDK-D08-06_health_fish_coastal |
ANSDK-D08-07_health_fish_migratory |
ANSDK-D08-08_health_fish_migratory_pelagic |
ANSDK-D08-09_mortality_birds |
ANSDK-D08-10_health_hardbottomfauna |
ANSDK-D08-12_health_softbottomfauna |
ANSDK-D08-13_CONTAMIN_input_atmos |
ANSDK-D08-14_CONTAMIN_INPUT_point_sources |
ANSDK-D08-17_CONTAMINAN_water |
ANSDK-D08-18_CONTAMINAN_sediment |
ANSDK-D08-19_CONTAMINAN_species |
| Q4g - Sub-programmes | Sub-programme name | Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - health status |
Mobile species - mortality/injury rates from other human activities |
Benthic species - health status |
Benthic species - health status |
Contaminant inputs - from atmosphere |
Contaminant inputs - land-based sources |
Contaminant levels - in water/sediment |
Contaminant levels - in water/sediment |
Contaminant levels - in species, including seafood |
| Q4k - Monitoring purpose | StateImpact |
StateImpact |
Activities |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
StateImpact |
Pressurse |
StateImpact Pressurse |
Pressurse Measures |
Pressurse |
StateImpact Pressurse |
Pressurse Measures |
Pressurse Measures |
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| Q4l - Links of monitoring programmes of other Directives and Conventions |
http://www.vildtsundhed.dk/english/Activities/Surveillance
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The surveys aim is to provide ICES assessment and science groups with consistent and standardized data for examining spatial and temporal changes in (a) the distribution and relative abundance of fish and fish assemblages; and (b) of the biological parameters of commercial fish species for stock assessment purposes.
In terms of groundfish surveys coordinated by IBTS, the main objectives are to:
1 ) To determine the distribution and relative abundance of pre‐recruits of the main commercial species with a view of deriving recruitment indices;
2 ) To monitor changes in the stocks of commercial fish species independently of commercial fisheries data;
3 ) To monitor the distribution and relative abundance of all fish species and selected invertebrates;
4 ) To collect data for the determination of biological parameters for selected species;
5 ) To collect hydrographical and environmental information;
6 ) To determine the abundance and distribution of late herring larvae (February North Sea survey).
http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20%28SISP%29/SISP1-IBTSVIII.pdf.
The survey is part of the DCF - obligation under the CFP |
The Danish Sea Sampling Program is the main source for information concerning discards. Scientific observers are on board commercial vessels during regular fishery. All relevant information concerning catch, vessel and gear characteristics, mesh size and selective gear devices, fishing ground, weather, ownership etc. are collected. All observers have a detailed manual describing the procedure for handling the catch on board. The data are used for estimating the total discard by number and weight by species, age group, area, quarter and métiers. The primary sampling unit was in 2014 was vessel. The selection of vessels for sampling is described below.
As a part of the program a limited part of the gillnet fleet is conducting self-sampling. These vessels are relatively small and it is therefore difficult to conduct a traditional observer trip. They are all conducting 1 day trips. An arrangement has been made with a selected number of vessels where DTU Aqua at randomly chosen days calls the fishermen and ask them to bring all discard to land where it will be handled as a normal discard trip. On one of the vessels an observer is onboard to have a reference. A danish manual is avalible. |
The purpose of the sand eel dredge survey is to collect sand eels buried in the seabed and compare catches (number and age composition) with the previous year's collections to assess year class strength of the lesser sand eel (Ammodytes marinus) in the different areas adopted by ICES in 2009. Data from the dredge survey is the basis for calculating a 0-group index, which is used in stock assessment. The 2014 survey is planned to be conducted with the commercial fishing vessel Salling. All species are speified and counted and weighted and station information with depth and temperature is recorded. On all new positions a bottom sample (a Van Veen grab) is taken to determinied the sediment type.
- 15 days at sea
- 165 dredge hauls and 40 sediment grab sample distributed over 55 planned sample positions . The 2013 survey program is attached. |
NOVANA
OSPAR CEMP
HELCOM COMBINE
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ICES Working Group of International Pelagic surveys (WGIPS) has conducted a guide to the methodologies adhered to during the planning, execution and analysis phases of WGIPS coordinated surveys. The manual is not yet avalible in an online version but will be attached as an appendix. The survey coordination and documentation is done in this ICES working group and the details can be found in the ICES repport:
http://www.ices.dk/sites/pub/Publication%20Reports/Expert%20Group%20Report/SSGESST/2014/WGIPS14.pdf.
The survey aims to provide an annual estimate of the distribution, abundance and population structure to inform the assessment of the following herring and sprat stocks: Western Baltic Spring Spawning herring (in IV and IIIa), North Sea Autumn Spawning herring (in IV and IIIa), West of Scotland herring (in VIaN), Malin Shelf herring (in VIaN-S and VIIb,c), North Sea sprat (in IV) and Sprat in IIIa.
The derived estimates and age structure of herring and sprat are used as tuning indices in the respective assessments and are submitted annually to the HAWG. The Danish contribution to the survey is in Skagerrak and Kattegat. |
ICES Working Group of International Pelagic surveys (WGIPS) has conducted a guide to the methodologies adhered to during the planning, execution and analysis phases of WGIPS coordinated surveys. The manual is not yet avalible in an online version but will be attached as an appendix. The survey coordination and documentation is done in this ICES working group and the details can be found in the ICES report:
http://www.ices.dk/sites/pub/Publication%20Reports/Expert%20Group%20Report/SSGESST/2014/WGIPS14.pdf.
The survey objectives are listed below:
• Carry out a pre-determined survey cruise track
• Determine an age stratified estimate of relative abundance of herring within the survey area
• Determine an age stratified estimate of relative abundance of blue whiting within the survey area
• Collect biological samples from directed trawling on insonified fish echotraces to determine age structure and maturity state of the herring stock
• Collect physical oceanography data from vertical profiles (CTD).
• Plankton sampling (WP2 and Dyedi)
A survey manual is included as an appendix MANUAL FOR INTERNATIONAL PELAGIC SURVEYS (IPS) page 7-12 |
http://naturstyrelsen.dk/naturoplevelser/jagt/tilskadekommet-vildt/beredskabsplan-for-havpattedyr-og-havfugle/ http://naturstyrelsen.dk/media/nst/Attachments/Beredskabsplanforhavpattedyrmarts2012.pdf
There is established a contingency plan designed to ensure a coordinated and effective action on marine mammals and seabirds in an emergency or in case of strandings in the country.
An effective contingency plan is an important prerequisite for being able to take steps to mitigate or avert the effects of, for example, an oil disaster at sea or deaths of marine mammals.
The Danish contingency plan for marine mammals and seabirds have two main functions: 1) to build a knowledge base that makes it possible to prevent and 2) to monitor an evolving situation and take the necessary measures so that the sick, stranded and oil-contaminated animals do not suffer unnecessarily. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.3 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.10 and 8.11 shows the position of the stations. 50% of the stations are in the BALDK area and 50% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Shellfish Waters Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
Details can bee found in The national survey program (NOVANA):
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Table 8.3 show total station in Danish Water, water samples per station, parameter analyzed and the frequent of sampling. Figur 8.10 and 8.11 shows the position of the stations. 50% of the stations are in the BALDK area and 50% of the stations are in ANSDK area.
Technical manual for the marine survey
http://bios.au.dk/videnudveksling/til-myndigheder-og-saerligt-interesserede/fagdatacentre/fdcmarintny/ta2011-2015/
Describe the procedure for sampling in the field and the quality control of the datasets collected.
The program contribute to the implementation of the Waterframe Directive, Habitat Directive, The Birds Directive, Seafood Directive, The Trilateral Wadden Sea Program and the Sea Convention. The national survey program NOVANA is coordinated with both HELCOM and OSPAR. |
The Danish monitoring program for air quality and atmospheric deposition contrubutes to the following other programmes: The EMEP monitoring program under CLRTAP, OSPAR, PARCOM and the monitoring in relation to the EU air quality directive (2008/50/EC). |
Water framework directive
IPPC-directive
COUNCIL DIRECTIVE of 4 May 1976 on pollution caused by certain dangerous substances discharged into the aquatic environment of the Community (76/464/EEC)
OSPAR
HELCOM
Stockholmkonvention
The strategy in the monitoring programme is meeting of all obligations and needs within the same programme if possible. |
NOVA national monitoring program, Randers Fjord.
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NOVANA
OSPAR CEMP
HELCOM COMBINE
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NOVANA
OSPAR CEMP
HELCOM COMBINE
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| Q5c - Features | Q5c - Habitats |
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| Q5c - Features | Q5c - Species list |
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| Q5c - Features | Q5c - Physical/Chemical features | |||||||||||||||
| Q5c - Features | Q5c - Pressures |
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| Q9a - Elements |
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| 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 |
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| Q9b - Parameters monitored (state/impact) | Species population size |
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| Q9b - Parameters monitored (state/impact) | Species population characteristics |
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| Q9b - Parameters monitored (state/impact) | Species impacts |
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| Q9b - Parameters monitored (state/impact) | Habitat distribution | |||||||||||||||
| Q9b - Parameters monitored (state/impact) | Habitat extent | |||||||||||||||
| Q9b - Parameters monitored (state/impact) | Habitat condition (physical-chemical) |
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| Q9b - Parameters monitored (state/impact) | Habitat condition (biological) |
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| Q9b - Parameters monitored (state/impact) | Habitat impacts |
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| Q9b - Parameters monitored (pressures) | Pressure input |
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| Q9b - Parameters monitored (pressures) | Pressure output |
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| Q9b - Parameters monitored (activity) | Activity |
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| Q9b Parameters monitored (other) | Other |
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| Q41 Spatial scope | MSland_FW WFD_TW WFD_CW TerritorialWaters |
EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
EEZ BeyondMSwaters |
WFD_CW |
EEZ BeyondMSwaters |
BeyondMSwaters |
MSland_FW WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters EEZ |
MSland_FW WFD_TW WFD_CW TerritorialWaters |
MSland_FW |
WFD_TW WFD_CW |
WFD_CW TerritorialWaters EEZ |
WFD_CW TerritorialWaters |
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| Q4j - Description of spatial scope | The National Monitorin Progrmme for Water and Nature is aiming at documenting impacts of the current measures, as well as establishing a basis for future managerial decision-making. |
IBTS is an international ICES coordinated survey, were Denmark gets appointed stations in Danish EZ zone as well as in international water in the North Sea. For every survey conducted a new list of stations is appointed and the area covered can vary between surveys. However, as a standard Denmark is conducting 18*2 days survey each year and this corresponds to 40 fishing stations and 80 plankton stations in the 1st quarter survey and 50 fishing stations and 0 plankton stations in the 3rd quarter survey. An international ICES manual is followed and a link to the newest version is added. DTU Aqua is participating in the ICES group (IBTSWG) coordinating the survey.
http://www.ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20%28SISP%29/SISP1-IBTSVIII.pdf |
Commercial vessels are selected randomly and success rate is recorded. Success rate is defined as the number of fishermen willing to participate in allowing the observers to come onboard. A new sampling system was introduced in 2011, where vessels are selected on a stratified random basis, based on last year’s data. For each métier and quarter a vessel selection spreadsheet has been computed and the change of selecting a vessel are weighted with the amount of trips conducted in the same quarter and area one year earlier. When a vessel is selected by the computer the observers are oblique to call the skipper to ask for the possibility to conduct an observer trip with his vessel. As the system is weighting the amounts of trips conducted by the vessel it is possible to select the same ship more than once within a quarter.
The fishermen answers are registered in a log. If a skipper decisively refuses to have an observer on board he is not contacted again within that year even though the ship is selected again by the system. However, the ship is registered with the same answer. If the skipper says “no” but is given a more vague answer (try again later or it is not fitting very good right now) he will be called again the next time the vessel is being selected by the system. |
The sand-eel survey is conducted on sandbanks in the North Sea where sand eel is or has been present historically. The stations have been selected in cooperation with the industry and are fixed stations. If new stations are added to the survey sediment sample is taken to confirm that the bottom environment is suitable for sand eels. |
In representative coastal areas, coordinated with the monitoring activities on contaminnant levels in fish. |
The purpose is to provide acoustic abundance estimates of herring and sprat in the North Sea (eastern part), Skagerrak and Kattegat. |
This survey is carried out in order to investigate abundance, distribution and migrations of the Atlanto-Scandian herring, blue whiting and other pelagic fish in the Norweigian Sea and adjacent waters . Furthermore, hydrographical conditions and plankton abundance are monitored. The survey was coordinated with Norway as an international survey with participation of Norway, Iceland, Faroe Islands and EU, where the Danish R/V Dana conducted the EU survey part. The survey is carried out as a joint EU survey with participation of UK, Ireland, Netherlands, Germany, Sweden and Denmark. |
All costal areas
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The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Stations in open waters located in relation to international shipping lanes. In coastal waters stations are located in representative areas, e.g. coordinated with program on contaminant-levels |
The program including rationale for the geographic scope can be found here:
http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/
Stations in open waters located in relation to international shipping lanes. Stations in coastal waters staions are located in representative areas, e.g. coordinated with program on contaminant-levels |
The Danish monitoring program for air quality and depositons is based on a few coastal fixed measurements stations where concentrations in air and wetdeposition is measured. The results from these measurements is in a simple way extrapolateed to cover the Danish land areas and the inner Danish waters in this context only Kattegat - thus not Skagerrak and the North Sea). For organic cantaminants only measurents of wet deposition a two measurements sites is carried out. |
The programme is set up in order to cover the whole country and therefore also for the reporting area. Descibed in chap. 3 in the description of the programme: http://naturstyrelsen.dk/media/nst/Attachments/NOVANA_2del.pdf |
Transect from Harbour.
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Danish part of OSPAR convention.
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Danish part of OSPAR convention. Mussel stations mainly coastal, fish stations more open stations in the North Sea. |
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| Marine Unit IDs |
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| Q4h - Temporal scope | Start date- End date | 1932-9999 |
1991-9999 |
1995-9999 |
2004-9999 |
2004-9999 |
2006-9999 |
2004-9999 |
1991-9999 |
1998-9999 |
1998-9999 |
1989-9999 |
1998-9999 |
2001-2003 |
1998-9999 |
1998-9999 |
| Q9h - Temporal resolution of sampling |
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| Q9c - Monitoring method | Passive disease surveillance in collaboration between The Danish Nature Agency and The National Veterinary Institute. |
ICES methods. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. Other parameter measured in connection to health is condition to commarcial species. This is monitored over time to detect changes in health and growth. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory. |
In the manual all relevant information on the sampling type can be found. However, all fish/ animals are specified to species or species group counted and weighted and station information with depth and temperature is recorded. On all new positions a bottom sample (a Van Veen grab) is taken to determinied the sediment type. |
Method according to The Marine Topic Centre (M-FDC) technical guidelines (in Danish): TA M26 Biologisk effektmonitering i fisk
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M26_Biologisk_effektmonitering_i_fisk__ver_1_.pdf |
ICES methods - following the international coordinated manual "MANUAL FOR INTERNATIONAL PELAGIC SURVEYS (IPS) " Other parameter measured in connection to health is condition in the pelagic species. This is monitored over time to detect changes in health and growth. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory. At sea the herrings aged are also analysed for fungus. |
ICES methods - following the international coordinated manual "MANUAL FOR INTERNATIONAL PELAGIC SURVEYS (IPS) " Biological sampling is carried out with large og midsized pelagic midwater trawls (countrydependent), with a vertical opening of 25-35 m. Trawl metrics are monitored using a net sonde. All components of the catch from the trawl hauls is sorted and weighed; fish and other taxa are identified to species level. Fish samples are divided into species composition by weight. Length frequency and length weight data is collected for each component of the catch. Length measurements of herring, and blue whiting to be taken to the nearest 0.5cm below.
Biological sampling is used to verify the composition of echotraces during echo integration. Decisions to fish on particular echotraces are largely subjective and an attempt should be made to target echotraces low density scattering layers not just high density shoals. No bottom trawl gear is used during this survey. Other parameter measured in connection to health is condition in the pelagic species. This is monitored over time to detect changes in health/ growth. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory. |
In case ofan oil spill where oiled birds are registered, the total number will be estimated and species registered. Samples of wings will be collected for age estimate http://www2.sns.dk/udgivelser/2003/havpattedyr/beredskabsplan.pdf |
"1) OSPAR JAMP guideline on contaminant specific effects, Tecnical annex 3 on TBT-specific effects.
2) ICES TIMES guideline on lysosomal membrane stability. Both guidelines are incoorprated into the national monitoring guideline on either TBT-specific effects in marine snails and biological effects in mussels" |
"1) OSPAR JAMP guideline on contaminant specific effects, Tecnical annex 3 on TBT-specific effects
2) ICES TIMES guideline on lysosomal membrane stability. Both guidelines are incoorprated into the national monitoring guideline on either TBT-specific effects in marine snails and biological effects in mussels" |
The measurement methods for are based on the methods recommended under the EMEP monitoring program. |
The samples are collected according to national technical instructions. Link to the technical instructions on sampling in the monitoring programme on point sources: http://naturstyrelsen.dk/naturbeskyttelse/national-naturbeskyttelse/overvaagning-af-vand-og-natur/novana-program/ta-for-punktkilder/. Demands for sample handling are given in special specification, which are provided by the Reference Laboratory/the Danish Nature Agency. Link to method specifikations: http://www.reference-lab.dk/metodedatablade/metodedatablade-kemiske.aspx. Demands for the analyses are found in legislation: Bekendtgørelsen om kvalitetskrav til miljømålinger nr 231 af 5. marts 2014 https://www.retsinformation.dk/Forms/R0710.aspx?id=160496. |
NOVA monitoring guidelines for NOVA 1998-2005 program:
http://www2.dmu.dk/1_om_dmu/2_tvaer-funk/3_fdc_mar/programgrundlag/TekAnv2004_2009/Del2/TA04_2_8_MFS_havvand.pdf |
OSPAR Aggrement 2002-16, JAMP Guidelines for Monitoring Contaminants in Sediments (rev. 2011).
www.ospar.org in “Program and measures” under “aggrements”, incoorporated into technical annexes for the national NOVANA program
http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M24_Miljoefarlige_stoffer_i_sediment_ver1.pdf |
OSPAR Aggrement 2002-16, JAMP Guidelines for Monitoring Contaminants in Sediments (rev. 2011). www.ospar.org in “Program and measures” under “aggrements”, incoorporated into technical annexes for the national NOVANA program http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M25_Miljoefarlige_stoffer_i_fisk.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M26_Biologisk_effektmonitering_i_fisk__ver_1_.pdf http://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M28_Biologisk_effektmonitering_i_muslinger__VERSION_2_.pdf |
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| Q9d - Description of alteration to method | Other parameter measured in connection to health is condition in the demersal species. This is monitored over time to detect changes in health. Furthermore, all herring aged are also analysed for the parasite nematode Anasaki in the laboratory. |
Other parameter measured in connection to health is condition in the demersal species. This is monitored over time to detect changes in health. No chemicals or pollutant concentration is meassured. |
Acoustic data are collected using a Simrad EK60 scientific echosounder. Split-beam transducers are mounted on the various vessels in different configurations. Several operating frequencies are used during the surveys (e.g. 18, 38, 120 and 200 kHz) for trace recognition purposes, but with 38 kHz data used to generate the abundance estimate All frequencies are to be calibrated prior to the survey. Details to be found in the manual. |
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| Q9e - Quality assurance |
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| Q9f - Quality control | Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
Unknown |
DelayedValidation |
DelayedValidation |
OtherQC |
DelayedValidation |
DelayedValidation |
DelayedValidation |
DelayedValidation |
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| Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | 100 |
0.67 |
50 |
2.5 |
100 |
90 |
90 |
20 |
100 |
10 |
75 |
75 |
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| Q9g - Spatial resolution of sampling | Q9g - No. of samples | Not determined - passive sampling |
around 150 trips are conducted on an annual basis and this corrispond to 325 days at sea. Indicating that 1 trip equals to 0.67%
From minimum 1 station per day we sample all species with length and weight and only selected speces for age |
9 |
As described above |
10 |
20 |
Measurements covers the entire callendar year. The estimated despositions for deposition to Danish land areas and Inner Dansih Waters are total annual deposition. |
2 samples/station/year
direct outlet: 7 stations
indirect outlet: 4 stations |
3 |
20 |
25+4 (mussels+fish) |
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| Q9i - Description of sample representivity | In first quarter survey we sample 40 fishing stations and 80 plankton stations and 50 fishing stations and 0 plankton stations in the 3rd quarter survey.
From each station we sample all species with length and weight and only selected speces (see appendix 1a) for age and maturity |
In 2014, 19 fishing days are planned |
The survey is conducted as a acustic survey and trawl samples are only taken when it can be detected on the acustic. The survey has planned to conduct 40 fishing stations and 20 planktonic stations each year. This indicates that 1 fishing station will have the influence of 2.5%.
The fish sample obtained from the trawl catch is divided into species by weight and by number. Length measurements are taken to the nearest 0.5 cm below for sprat and herring (and to the whole cm below for other species). For herring and sprat either representative or length stratified samples are taken for maturity, age (otolith extraction) and weight.
The biological sampling includes measures to allow discrimination amongst different stocks of herring. In the Danish part of the survey the total herring estimate is divided into North Sea Autumn Spawners and Western Baltic Spring Spawners. The mean weights and mean lengths used are the same for the two stocks as they are not divided on an individual basis. The split is based on vertebral counts in the Norwegian part and on otolith shape analysis in the Danish survey area. |
The survey is conducted as an acustic survey and trawl samples are only taken when it can be detected on the acustic. The survey has planned to conduct 10 fishing stations and 35 planktonic stations each year. This indicates that 1 fishing station will have the influence of 10% and a plankton station will influence around 3% of the total stations carried out by Denmark.
Catches from trawl hauls are sorted and weighed; fish are identified to species level, when possible, and other taxa to higher taxonomic levels. Normally a subsample of 30–100 herring and blue whiting are sexed, aged, and measured for length and weight, and their maturity status is estimated using established methods. An additional sample of 70–300 fish is measured for length. |
The estimated depositions cover the Dansih land areas and the Inner Danish Waters. Two measurement stations for heavy metals are linked to the North Sea. One measuremtent station situated about 20 km from the west coast of Jutland and one is situated on the small island Anholt in Kattegat. Measurements of wet depostions of organic contaminants are carried out at Roskilde and Sepstrup Sande in mid Jutland |
The stations are for most parts used to give a spatial more than time-trend view of concentrations/pressures within different marine areas. Some stations are analysed in duplicates from two subsamples at the same location, others are sampled within the same area in relative close proximity to give an estimate of the area variance. |
Fish stations are timetrend, 4 mussel stations timetrend stations (revisited yearly). Other mussel stations are placed every year to extend spatial coverage and support for MPAs or areas in risk of higher pressures |
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| Q10a - Scale for aggregation of data |
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| Q10b - Other scale for aggregation of data | n/a |
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| Q10c - Access to monitoring data | Q10c - Data type | ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData |
Simulated |
Simulated |
UnprocessedData |
UnprocessedData ProcessedData |
UnprocessedData ProcessedData |
ProcessedData |
ProcessedData |
UnprocessedData ProcessedData |
ProcessedData DataProducts |
ProcessedData DataProducts |
| Q10c - Access to monitoring data | Q10c - Data access mechanism | LocationInternationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationNationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationInternationalDC |
URLview |
LocationNationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationNationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationInternationalDC |
| Q10c - Access to monitoring data | Q10c - Data access rights | Open |
Open |
RestrictedSpecific |
RestrictedSpecific |
Open |
RestrictedSpecific |
RestrictedSpecific |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
Open |
| Q10c - Access to monitoring data | Q10c - INSPIRE standard | SeaRegions SpeciesDistribution |
OceanographicFeatures SpeciesDistribution |
OceanographicFeatures SpeciesDistribution |
HabitatsBiotopes SpeciesDistribution |
OceanographicFeatures |
OceanographicFeatures SpeciesDistribution |
HabitatsBiotopes OceanographicFeatures SpeciesDistribution |
SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
HabitatsBiotopes OceanographicFeatures SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions |
SeaRegions |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
OceanographicFeatures SeaRegions |
| Q10c - Access to monitoring data | Q10c Date data are available | 2015-12 |
2015-04 |
2015-04 |
2015-02 |
2015-12 |
2015-03 |
2015-03 |
2015-12 |
2015-04 |
2015-04 |
1990-01 |
2015-12 |
2014-12 |
1999-01 |
1999-01 |
| Q10c - Access to monitoring data | Q10c - Data update frequency | Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Asneeded |
2yearly |
2yearly |
Yearly |
Yearly |
2yearly |
Yearly |
Yearly |
| Q10d - Description of data access | Data will be reported in yearly report under the National Monitoring Programme for Water and Nature as well as in the fortcomin MSFD artciel 8 intial assessment due in 2018 |
In ICES DATRAS database.
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In ICES Regional data base (RDB).
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Data will be available for managerial purposes of sandeels management at national data center at DTU Aqua, but will also be made available in the forthcoming MSFD art. 8 initial assessment due in 2018. |
Data are reported in yearly reports under the National Monitoring Programme for Water and Nature as well as in the forthcomin MSFD art 8 initial assessment due in 2018 |
ICES is presently working on constructing a database where all aquatic data can be uploaded and stored. Presently DTU Aqua is hosting this database. |
ICES is presently working on constructing a database where all aquatic data can be uploaded and stored. Presently DTU Aqua is hosting this database. |
n/a
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Yearly National report under the National Monitoring Programme for Water and Nature, NOVANA, and in the forthcoming MSFD art 8 initial assessment in 2018 |
Yearly National report. under the National Monitoring Programme for Water and Nature as well as in the forthcoming MSFD art 8 initial assessement due in 2018 |
Data are published yearly under the National Monitopring Prgroamme for Water and Nature, as well as in the forthcoming MSFD art 8 initial assessment due in 2018. |
Data are published in yearly reports under the NAtional Monitoring Programme for Water and Nature, as well as in the forthcoming MSFD art 8 initial assessment due in 2018 |
Data and information will be available in yearly reportings under the National Monitoring Programme for Water and Nature, and in the forthcoming article 8 assessment in 2018. |
data is published in yearly reports under the NAtional Monitoring Programme for Water and NAture, as well as in the forthcoming MSFD art. 8 initial assessment due in 2018 |
Data will be reported in yearly reports under the National Monitoring Progrqmme for Water and NAture, NOVANA and in the forthcoming MSFD art 8 initial assessment in 2018. |
|
Descriptor |
D8 |
D8 |
D8 |
D8 |
D8 |
D8 |
D8 |
D8 |
D8 |
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Monitoring strategy description |
Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
|
Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
|
Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
|
Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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Formålet med overvågningsprogrammet af forurenende stoffer er, at følge om koncentrationen af de forurenende stoffer, overstiger niveauer, der medfører forureningsvirkninger i miljøet. Miljøfarlige stoffer stammer fra mange forskellige aktiviteter, som kan være helt eller delvis regulerede, men også akutte forureningshændelser, som stammer fra uheld og spild af fx kemikalier og olie. Overvågningen består af to dele 1) overvågning af en lang række miljøfarlige stoffer samt test for biologiske effekter, og 2) overvågning i forbindelse med akutte forureningshændelser.
Overvågningsprogrammet har til formål at sikre, at miljøtilstanden, som den er defineret i basisanalysen for Danmarks Havstrategi II, løbende kan følges i de danske havområder. Overvågningsprogrammet og basisanalyserne skal sammen danne grundlag for udarbejdelsen af de indsatsprogrammer, der skal sikre opfyldelse af miljømålene. Overvågningen vil endvidere føre til en vurdering af indsatsprogrammets foranstaltninger i forhold til opnåelse eller opretholdelse af god miljøtilstand. Overvågningsprogrammet er således tilrettelagt for at vurdere fremskridt i forhold til GES, miljømål og indsatser.
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Coverage of GES criteria |
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 |
Gaps and plans |
Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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Der foreligger endnu ikke en akutplan for overvågning ved forureningshændelser, men, der vil først i den kommende overvågningsperioden udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser.
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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 |
Related measures |
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Coverage of measures |
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 monitoring programmes |
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Programme code |
DK-D08-01 |
DK-D08-01 |
DK-D08-02 |
DK-D08-02 |
DK-D08-03 |
DK-D08-03 |
DK-D08-04 |
DK-D08-05 |
DK-D08-05 |
Programme name |
Contaminant levels - in sediment |
Contaminant levels - in sediment |
Contaminant levels - in biota |
Contaminant levels - in biota |
Contaminant effects - in biota |
Contaminant effects - in biota |
Contaminant levels - acute pollution incidents |
Non-target screeninger |
Non-target screeninger |
Update type |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
New programme |
New programme |
Old programme codes |
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Programme description |
Sedimentprøver
Fra sedimentet udtages prøver fra den øverste centimeter, som typisk repræsenterer de sidste 3-7 års påvirkninger. Prøverne udtages minimum engang i perioden på forskellige stationer. Der overvåges i alt 4 kontrolstationer, 178 operationelle stationer og 15 havstrategistationer . Frekvens og udvalgte parametre findes i NOVANA 2017-21 programbeskrivelsen. For sedimentstationerne uden for 12 sømil, ligger der ti i Nordsøen til og fem stationer fordelt på Skagerrak (1), Kattegat (2), Ar-konabassinet (1) og øst for Bornholm (1). Desuden udvides stofgruppepakken på et udvalg af de eksisterende fjord- og kyststationer. De supplerende stationer og stofgrupper vil foruden øget geografisk dækning sikre, at de af havstrategien fokuserede miljøfarlige stoffer dels overvåges i både HELCOM og OSPAR-områderne og dels på kystnære såvel som på åbenvandsstationer.
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Sedimentprøver
Fra sedimentet udtages prøver fra den øverste centimeter, som typisk repræsenterer de sidste 3-7 års påvirkninger. Prøverne udtages minimum engang i perioden på forskellige stationer. Der overvåges i alt 4 kontrolstationer, 178 operationelle stationer og 15 havstrategistationer . Frekvens og udvalgte parametre findes i NOVANA 2017-21 programbeskrivelsen. For sedimentstationerne uden for 12 sømil, ligger der ti i Nordsøen til og fem stationer fordelt på Skagerrak (1), Kattegat (2), Ar-konabassinet (1) og øst for Bornholm (1). Desuden udvides stofgruppepakken på et udvalg af de eksisterende fjord- og kyststationer. De supplerende stationer og stofgrupper vil foruden øget geografisk dækning sikre, at de af havstrategien fokuserede miljøfarlige stoffer dels overvåges i både HELCOM og OSPAR-områderne og dels på kystnære såvel som på åbenvandsstationer.
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Biota
Muslinger
MFS opkoncentreres i muslinger, og målingerne repræsenterer et integreret niveau af stofferne over de sidste dage/måneder. Muslingeprøverne tages hvert andet år i tidsrummet oktober-november på 20 kontrolstationer. 178 stationer er omfattet af den operationelle overvågning og analyseres én gang over en femårig periode. Syv stationer er havstrategstationer, som analyseres hvert eller hvert andet år. Desuden er der tre supplerende stationer, hvorfra der analyseres for indholdet af dioxiner, dioxinlignende PCB’er og furaner en til to gange i perioden. Frekvens og udvalgte parametre findes i NOVANA 2017-21 programbeskrivelsen.
Fisk
For at vurdere mængden af miljøfarlige stoffer, som ophobes i de øverste led i fødekæden, analyseres også for miljøfarlige stoffer i fisk. Ålekvabbe eller sortmundet kutling, rødspætte og skrubbe er kystnære og stationære fisk, som på den baggrund er udvalgt som gode moniteringsorganismer i kystnære områder. For fisk måles MFS i tidsrummet oktober-januar, hvor 14 kontrolstationer analyseres hvert andet år og 178 operationelle stationer analyseres en til to gange over en femårig periode. Derudover er der 76 operationelle stationer hvor der specifikt undersøges for dioxiner, furaner og 12 dioxinlignende PCB’er i fisk. I regi af havstrategien overvåges foruden ovennævnte stoffer også for Polybromerede diphenylethere (PBDE) og Perfluorooctane sulphonate (PFOS) i fiskelever på tre stationer hvert år. Frekvens og udvalgte parametre findes i NOVANA 2017-21 programbeskrivelsen.
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Biota
Muslinger
MFS opkoncentreres i muslinger, og målingerne repræsenterer et integreret niveau af stofferne over de sidste dage/måneder. Muslingeprøverne tages hvert andet år i tidsrummet oktober-november på 20 kontrolstationer. 178 stationer er omfattet af den operationelle overvågning og analyseres én gang over en femårig periode. Syv stationer er havstrategstationer, som analyseres hvert eller hvert andet år. Desuden er der tre supplerende stationer, hvorfra der analyseres for indholdet af dioxiner, dioxinlignende PCB’er og furaner en til to gange i perioden. Frekvens og udvalgte parametre findes i NOVANA 2017-21 programbeskrivelsen.
Fisk
For at vurdere mængden af miljøfarlige stoffer, som ophobes i de øverste led i fødekæden, analyseres også for miljøfarlige stoffer i fisk. Ålekvabbe eller sortmundet kutling, rødspætte og skrubbe er kystnære og stationære fisk, som på den baggrund er udvalgt som gode moniteringsorganismer i kystnære områder. For fisk måles MFS i tidsrummet oktober-januar, hvor 14 kontrolstationer analyseres hvert andet år og 178 operationelle stationer analyseres en til to gange over en femårig periode. Derudover er der 76 operationelle stationer hvor der specifikt undersøges for dioxiner, furaner og 12 dioxinlignende PCB’er i fisk. I regi af havstrategien overvåges foruden ovennævnte stoffer også for Polybromerede diphenylethere (PBDE) og Perfluorooctane sulphonate (PFOS) i fiskelever på tre stationer hvert år. Frekvens og udvalgte parametre findes i NOVANA 2017-21 programbeskrivelsen.
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Biologiske effekter
De biologiske effekter af miljøfarlige stoffer undersøges ved forskellige biologiske effektindikatorer i marine snegle, muslinger, fisk og krebsdyr. Graden af imposex og intersex måles hos havsnegle og overvåges hvert andet år på 14 stationer. Derudover overvåges også for biologiske effekter hos ålekvabber og muslinger hvert år på to stationer. For så vidt angår effektovervågning af krebsdyr overvåges der på to effektstationer hvert år.
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Biologiske effekter
De biologiske effekter af miljøfarlige stoffer undersøges ved forskellige biologiske effektindikatorer i marine snegle, muslinger, fisk og krebsdyr. Graden af imposex og intersex måles hos havsnegle og overvåges hvert andet år på 14 stationer. Derudover overvåges også for biologiske effekter hos ålekvabber og muslinger hvert år på to stationer. For så vidt angår effektovervågning af krebsdyr overvåges der på to effektstationer hvert år.
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Akutplan
I den kommende overvågningsperiode udarbejdes en akutplan, som adresserer konkrete arbejdsgange og overvågningsaktiviteter i forbindelse med akutte forureningshændelser. I den kommende overvågningsperiode vil der blive nedsat en tværministeriel arbejdsgruppe, som kan bidrage til at fastlægge rammerne for udarbejdelsen af overvågningsprogrammet for akutte forureningshændelser.
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Non-target screeninger
Danmark deltager i et projekt om non-target screeninger. Projektet gennemføres under de regionale havkonventioner HELCOM og OSPAR. Igennem projektet skal det undersøges, om brugen af non-target screening kan identificere miljøfarlige stoffer i den marine fødekæde, - stoffer der ikke indgår i de rutinemæssige undersøgelser. Medlemslandende bidrager med allerede indsamlede prøver i form af muslinger, fisk og sediment. Efterfølgende sendes prøverne til analyselaboratoriet, som foretager non-target screening og analyse af, hvilke stoffer der er indeholdt i prøverne. Resultaterne kan efter-følgende anvendes til at vurdere, om yderligere stoffer fremadrettet bør medtages i den nationale overvågning. Samtidig kan resultaterne anvendes i regi af HELCOM og OSPAR til en vurdering af, om listerne over prioriterede miljøfarlige stoffer bør revurderes.
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Non-target screeninger
Danmark deltager i et projekt om non-target screeninger. Projektet gennemføres under de regionale havkonventioner HELCOM og OSPAR. Igennem projektet skal det undersøges, om brugen af non-target screening kan identificere miljøfarlige stoffer i den marine fødekæde, - stoffer der ikke indgår i de rutinemæssige undersøgelser. Medlemslandende bidrager med allerede indsamlede prøver i form af muslinger, fisk og sediment. Efterfølgende sendes prøverne til analyselaboratoriet, som foretager non-target screening og analyse af, hvilke stoffer der er indeholdt i prøverne. Resultaterne kan efter-følgende anvendes til at vurdere, om yderligere stoffer fremadrettet bør medtages i den nationale overvågning. Samtidig kan resultaterne anvendes i regi af HELCOM og OSPAR til en vurdering af, om listerne over prioriterede miljøfarlige stoffer bør revurderes.
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Monitoring purpose |
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Other policies and conventions |
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Regional cooperation - coordinating body |
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Regional cooperation - countries involved |
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Regional cooperation - implementation level |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Agreed data collection methods |
Joint data collection |
Joint data collection |
Monitoring details |
Data indsamles efter den akutte hændelse er forekommet.
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Projektet gennemføres under de regionale havkonventioner HELCOM og OSPAR. Igennem projektet skal det undersøges, om brugen af non-target screening kan identificere miljøfarlige stoffer i den marine fødekæde, - stoffer der ikke indgår i de rutinemæssige undersøgelser.
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Projektet gennemføres under de regionale havkonventioner HELCOM og OSPAR. Igennem projektet skal det undersøges, om brugen af non-target screening kan identificere miljøfarlige stoffer i den marine fødekæde, - stoffer der ikke indgår i de rutinemæssige undersøgelser.
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Features |
Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Adverse effects on species or habitats
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Adverse effects on species or habitats
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Acute pollution events
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Adverse effects on species or habitats
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Adverse effects on species or habitats
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Acute pollution events
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Contaminants - non UPBT substances
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Contaminants - UPBT substances
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Adverse effects on species or habitats
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Adverse effects on species or habitats
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Acute pollution events
|
Contaminants - non UPBT substances
|
Contaminants - UPBT substances
|
|
Contaminants - non UPBT substances
|
Contaminants - UPBT substances
|
Contaminants - non UPBT substances
|
Contaminants - UPBT substances
|
Adverse effects on species or habitats
|
Adverse effects on species or habitats
|
Acute pollution events
|
Contaminants - non UPBT substances
|
Contaminants - UPBT substances
|
|
Elements |
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|
GES criteria |
D8C1 |
D8C1 |
D8C1 |
D8C1 |
D8C2 |
D8C2 |
D8C3 |
D8C1 |
D8C1 |
Parameters |
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Parameter Other |
EROD, FAC (PAH-metabolitter), fejludviklede unger, |
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Spatial scope |
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Marine reporting units |
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|
|
Temporal scope (start date - end date) |
1998-9999 |
1998-9999 |
1998-9999 |
1998-9999 |
1998-9999 |
1998-9999 |
2014-9999 |
2020-9999 |
2020-9999 |
Monitoring frequency |
6-yearly |
6-yearly |
Yearly |
Yearly |
Yearly |
Yearly |
As needed |
As needed |
As needed |
Monitoring type |
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Monitoring method |
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Monitoring method other |
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M24_Miljoefarlige_stoffer_i_sediment_ver2.pdf |
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M24_Miljoefarlige_stoffer_i_sediment_ver2.pdf |
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M22_Miljoefarlige_stoffer_i_muslinger_ver2.pdf
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M25_Miljoefarlige_stoffer_i_fisk__version_2_.pdf |
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M22_Miljoefarlige_stoffer_i_muslinger_ver2.pdf
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M25_Miljoefarlige_stoffer_i_fisk__version_2_.pdf |
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M26_Biologisk_effektmonitering_i_fisk__ver_1_.pdf
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M27_Imposex_og_intersex_i_havsnegle_ver1.pdf
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M28_Biologisk_effektmonitering_i_muslinger__VERSION_2_.pdf |
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M26_Biologisk_effektmonitering_i_fisk__ver_1_.pdf
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M27_Imposex_og_intersex_i_havsnegle_ver1.pdf
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M28_Biologisk_effektmonitering_i_muslinger__VERSION_2_.pdf |
https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf |
https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf
Henvises til kommende HELCOM og OSPAR manualer. |
https://www2.mst.dk/Udgiv/publikationer/2020/07/978-87-7038-209-0.pdf
Henvises til kommende HELCOM og OSPAR manualer. |
Quality control |
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt af MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt af MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
I Danmark kvalitetssikres størstedelen af de danske overvågningsdata i den nationale database (VanDa) ved tre kvalitetssikringsniveauer:
1. Elektronisk kontrol – den automatiske kontrol alle indtastninger undergår, når der registreres data i VanDa
2. Faglig kontrol – automatisk/manuel vurdering af data og data serier i VanDa.
3. Fagdatacenter kontrol – manuel vurdering af data og dataserier udført af fagdatacentret.
Hvis data ikke indrapporteres til den nationale database kvalitetssikres data af konsulenten, der udfører overvågningsopgaven, samt MFVM efter metoderne beskrevet i nationale tekniske anvisninger eller internationale guidelines.
|
Data management |
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
I Danmark udvikles der lige nu en ny national database, som har til formål at samle og opbevare data fra vandmiljøovervågningen – herunder også overvågningen under havstrategien. Databasen forventes færdigudviklet i første halvår 2021. Efter en kvalitetssikring vil data blive gjort offentligt tilgængelige.
|
Data access |
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Related indicator/name |
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Contact |
cekan@mst.dk |
cekan@mst.dk |
cekan@mst.dk |
cekan@mst.dk |
cekan@mst.dk |
cekan@mst.dk |
cekan@mst.dk |
cekan@mst.dk |
cekan@mst.dk |
References |