Member State report / Art11 / 2014 / D10 / 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 |
GES Descriptor | D10 Litter |
Member State | Denmark |
Region/subregion | NE Atlantic: Greater North Sea |
Reported by | Danish Nature Agency |
Report date | 2014-10-15 |
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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Monitoring programme | Monitoring programme name | MP_D10 |
MP_D10 |
MP_D10 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
MP_D3 |
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Monitoring programme | Reference existing programme | |||||||||
Monitoring programme | Marine Unit ID |
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Q4e - Programme ID | ANSDK-D10 |
ANSDK-D10 |
ANSDK-D10 |
ANSDK-D03 |
ANSDK-D03 |
ANSDK-D03 |
ANSDK-D03 |
ANSDK-D03 |
ANSDK-D03 |
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Q4f - Programme description | Relevant monitoring on litter is already taking place. Experiences and data will be analysed to set up a programme covering both beaches, seabed, water column and biota. Focus will be on state to be able to determine if litter-levels are reduced.
LINK TIL PROGRAM+ evt. OSPAR/HELCOM |
Relevant monitoring on litter is already taking place. Experiences and data will be analysed to set up a programme covering both beaches, seabed, water column and biota. Focus will be on state to be able to determine if litter-levels are reduced.
LINK TIL PROGRAM+ evt. OSPAR/HELCOM |
Relevant monitoring on litter is already taking place. Experiences and data will be analysed to set up a programme covering both beaches, seabed, water column and biota. Focus will be on state to be able to determine if litter-levels are reduced.
LINK TIL PROGRAM+ evt. OSPAR/HELCOM |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes. |
The programme consists of a number of sub-programmes that are prepared in coordination with ICES. In addition the yearly programme may be supplemented to serve national managerial purposes. |
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Q5e - Natural variability |
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Q5d - Adequacy for assessment of GES | Q5d - Adequate data | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Q5d - Adequacy for assessment of GES | Q5d - Established methods | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Q5d - Adequacy for assessment of GES | Q5d - Adequate understanding of GES | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Q5d - Adequacy for assessment of GES | Q5d - Adequate capacity | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Q5f - Description of programme for GES assessment | In addition to ongoing activities on collecting and analyzing marine litter, a marine litter programme will be established aiming at
- registrating litter along 4 coastal stretches at the North Sea/Skagerrak, Kattegat and (in the Baltic Sea).
- analysis of microplastics in several marine areas
- macro and microplastiks in fish stomachs
- data that may eventually be used for modelcalculations of distribution of marine litter |
In addition to ongoing activities on collecting and analyzing marine litter, a marine litter programme will be established aiming at
- registrating litter along 4 coastal stretches at the North Sea/Skagerrak, Kattegat and (in the Baltic Sea).
- analysis of microplastics in several marine areas
- macro and microplastiks in fish stomachs
- data that may eventually be used for modelcalculations of distribution of marine litter |
In addition to ongoing activities on collecting and analyzing marine litter, a marine litter programme will be established aiming at
- registrating litter along 4 coastal stretches at the North Sea/Skagerrak, Kattegat and (in the Baltic Sea).
- analysis of microplastics in several marine areas
- macro and microplastiks in fish stomachs
- data that may eventually be used for modelcalculations of distribution of marine litter |
According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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According to coordination in ICES
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Q5g - Gap-filling date for GES assessment | By2018 |
By2018 |
By2018 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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Q5h - Plans to implement monitoring for GES assessment | An extended programme is under development. The programme will use existing data and monitoring activities and add relevant elements. The programme will be in place from 2015. |
An extended programme is under development. The programme will use existing data and monitoring activities and add relevant elements. The programme will be in place from 2015. |
An extended programme is under development. The programme will use existing data and monitoring activities and add relevant elements. The programme will be in place from 2015. |
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Q6a -Relevant targets | Q6a - Environmental target | DK_41_ANS DK_42_ANS DK_43_ANS |
DK_41_ANS DK_42_ANS DK_43_ANS |
DK_41_ANS DK_42_ANS DK_43_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
Q6a -Relevant targets | Q6a - Associated indicator | DK_41_ANS DK_42_ANS DK_43_ANS |
DK_41_ANS DK_42_ANS DK_43_ANS |
DK_41_ANS DK_42_ANS DK_43_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
DK_14_ANS DK_17_ANS DK_29_ANS DK_30_ANS DK_34_ANS DK_36_ANS DK_41_ANS DK_48_ANS |
Q6b - Adequacy for assessment of targets | Q6b_SuitableData | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Q6b - Adequacy for assessment of targets | Q6b_EstablishedMethods | N |
N |
N |
Y |
Y |
Y |
Y |
Y |
Y |
Q6b - Adequacy for assessment of targets | Q6d_AdequateCapacity | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Q6c - Target updating | Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
Y |
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Q6d - Description of programme for targets assessment | The forthcoming programme will be able to deliver data that will be relevant for regionally coordinated OSPAR and HELCOM assessments on the occurence of marine litter. |
The forthcoming programme will be able to deliver data that will be relevant for regionally coordinated OSPAR and HELCOM assessments on the occurence of marine litter. |
The forthcoming programme will be able to deliver data that will be relevant for regionally coordinated OSPAR and HELCOM assessments on the occurence of marine litter. |
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
The programme provides data on key indicators for descriptor 3. Existing dta series will provide information on variability, trends and distances from levels recorded previously and/or provide data for the assessment of possible progress towards reaching targets. |
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Q6e - Gap-filling date for targets assessment | By2018 |
By2018 |
By2018 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
By2014 |
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Q6f - Plans to implement monitoring for targets assessment | An extended programme is under development. The programme will use existing data and monitoring activities and add relevant elements. The programme will be in place from 2015 |
An extended programme is under development. The programme will use existing data and monitoring activities and add relevant elements. The programme will be in place from 2015 |
An extended programme is under development. The programme will use existing data and monitoring activities and add relevant elements. The programme will be in place from 2015 |
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Q7a - Relevant activities |
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Q7b - Description of monitoring of activities | The forthcoming programme will be able to deliver data that will be relevant for regionally coordinated OSPAR and HELCOM assessments on the occurence of marine litter. |
The forthcoming programme will be able to deliver data that will be relevant for regionally coordinated OSPAR and HELCOM assessments on the occurence of marine litter. |
The forthcoming programme will be able to deliver data that will be relevant for regionally coordinated OSPAR and HELCOM assessments on the occurence of marine litter. |
According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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According to guidelines of ICES agreements
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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 |
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Q8a - Links to existing Monitoring Programmes |
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Reference sub-programme | Sub-programme ID | ANSDK-D10-04_LITTER_beach |
ANSDK-D10-05_LITTER_fulmars |
ANSDK-D03-04_mortal_fisheries_birds |
ANSDK-D03-05_mortal_fisheries_porpoise |
ANSDK-D03-06_mortal_fisheries_seals |
ANSDK-D03-08_mortal_fish_coastal |
ANSDK-D03-09_mortal_fish_migrat_pelagic |
ANSDK-D03-10_mortal_fish_offsh_commercial |
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Reference sub-programme | Sub-programme name | Litter - characteristics and abundance/volume |
Litter inputs - land-based (riverine) sources |
Litter - characteristics and abundance/volume |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Q4g - Sub-programmes | Sub-programme ID | ANSDK-D10-04_LITTER_beach |
ANSDK-D10-05_LITTER_fulmars |
ANSDK-D03-04_mortal_fisheries_birds |
ANSDK-D03-05_mortal_fisheries_porpoise |
ANSDK-D03-06_mortal_fisheries_seals |
ANSDK-D03-08_mortal_fish_coastal |
ANSDK-D03-09_mortal_fish_migrat_pelagic |
ANSDK-D03-10_mortal_fish_offsh_commercial |
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Q4g - Sub-programmes | Sub-programme name | Litter - characteristics and abundance/volume |
Litter inputs - land-based (riverine) sources |
Litter - characteristics and abundance/volume |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Mobile species - mortality/injury rates from fisheries (targeted and/or incidental) |
Q4k - Monitoring purpose | Pressurse |
Pressurse |
Activities |
Activities |
Activities |
StateImpact |
StateImpact |
Activities |
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Q4l - Links of monitoring programmes of other Directives and Conventions | The monitoring is contributing to the agreements under the OSPAR convention. OSPAR pre-CEMP Appendix 15 - Beach Litter |
OSPAR Convention. Monitoring by Contracting Parties started for the purpose of the EcoQO for the North Sea. |
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 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 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. |
Catches from the recreational fisheries are registered on a voluntary basis by ”key” fishermen at fixed stations in most parts of the Danish coasts. The catches are performed with standard gillnets (one mesh size, 65 mm) and/or fyke nets, with up to 3 samples monthly in the beginning of each month, and from around April to November. Because of the mesh size used, the gillnets sample mostly adults, whereas juveniles of flounder and cod may be caught in the fyke nets. At present about 100+ fishers are invovled in the project. the last report with a detailed description can be downloaded:
http://orbit.dtu.dk/files/100552186/Publishers_version.pdf |
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 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. |
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. |
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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 |
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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 | |||||||||
Q9b - Parameters monitored (pressures) | Pressure output |
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Q9b - Parameters monitored (activity) | Activity |
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Q9b Parameters monitored (other) | Other | |||||||||
Q41 Spatial scope | MSland_FW WFD_CW EEZ |
EEZ |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
WFD_CW |
BeyondMSwaters |
WFD_CW EEZ BeyondMSwaters |
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Q4j - Description of spatial scope | The Danish monitoring of beach litter has so far not been conducted within the national monitoring program and has thus been conducted on a smaller scale. |
The sampling area is located within the main distribution area of the fulmar in the Danish waters |
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. |
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. |
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. |
Project has been launched in order to ascertain the species distribution along the coastal strips of Denmark. |
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. |
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. |
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Marine Unit IDs |
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Q4h - Temporal scope | Start date- End date | - |
2001-9999 |
2002-2011 |
1995-9999 |
1995-9999 |
1995-9999 |
2005-9999 |
2004-9999 |
1995-9999 |
Q9h - Temporal resolution of sampling |
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Q9c - Monitoring method | OSPAR beach litter guideline
http://www.ospar.org/documents/dbase/decrecs/agreements/10-02e_beachlitter%20guideline_english%20only.pdf |
Handbook for the application of Ecological Quality Objectives in the North Sea.
Second Edition - 2009.
OSPAR Biodiversity Series Publication 307/2009 |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
In this project 102 voluntary recreational fishermen participated, using either gillnets, fyke-nets or both gear types. Note that the results resented in this report represent catches reported by recreational fishermen. All species have caught have been registered and length measurements have been taken. The results showed a high fish biodiversity in Danish coastal waters. A total of 49 fish species were registered in gillnets and 72 in fyke-nets. This projec represent the largest and longest time series on catches in gillnets and fyke-nets along the Danish coasts. As age and length and weight by age are followed on a regular basis it is possible to follow the development over time, to estimate if the population is in a healthy state. |
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. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized between years. |
ICES methods for best pratice in on shore and at sea sampling. SGPIDS, WKPICS, PGCCDBS, RCM Baltic and RCM North Sea. As age and length and weight by age is followed continually it is possible to follow the development over time, to estimate if the population is in a healthy state.Data derived from this program is used in stock assessment to estimate the fishing mortality on the commercial important stocks. |
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Q9d - Description of alteration to method | This program is registering all birds by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch of breeding or wintering birds by is mainly registration if the bird is catch in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of birds. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
This program is registering all mammals by species caught in the commercial vessels were the program is operating. However, the program is not design to target by-catch mammals it is mainly registration if the mammals are caught in the commercial gear. Furthermore, it should be highlighted that the main part of the targeted fleet in this program is trawlers and not the gillnetters who would probably have a larger rate of by-catch of mammals. |
The method can be seen in the manual. No age are estimated but length and weight. The data can be used to evaluate the development in the length and weight distribution for commercial species over time, as the gears are standardized. |
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 |
Unknown |
RealandDelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
DelayedValidation |
RealandDelayedValidation |
RealandDelayedValidation |
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Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | 1 |
25 |
0.67 |
0.67 |
0.67 |
0.3 |
0.67 |
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Q9g - Spatial resolution of sampling | Q9g - No. of samples | 1 |
Opportunity basis (app. 10-100 birds a year) |
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 species for age. |
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. |
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. |
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 species for age. |
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Q9i - Description of sample representivity | 103 fishermen are participating with 3 sites eac. Indicating that each site represent 0.3% of the total.
In total 52,000 individuals were caught in the last three year. Eelpout topped the list of species most frequently caught, mostly in fyke-nets. Next on the list was flounder with 23,000 individuals being caught over 3 years. An equal number of cod and eel were caught; 9,000 individuals. The catches reflect the fac. |
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. |
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Q10a - Scale for aggregation of data |
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Q10b - Other scale for aggregation of data | . |
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Q10c - Access to monitoring data | Q10c - Data type | UnprocessedData |
UnprocessedData |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData DataProducts |
ProcessedData |
Simulated |
ProcessedData DataProducts |
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Q10c - Access to monitoring data | Q10c - Data access mechanism | URLview |
URLview |
LocationInternationalDC |
LocationInternationalDC |
LocationInternationalDC |
LocationNationalDC |
LocationInternationalDC |
LocationInternationalDC |
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Q10c - Access to monitoring data | Q10c - Data access rights | Open |
Open |
RestrictedSpecific |
RestrictedSpecific |
RestrictedSpecific |
RestrictedSpecific |
RestrictedSpecific |
RestrictedSpecific |
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Q10c - Access to monitoring data | Q10c - INSPIRE standard | SeaRegions |
SeaRegions |
HabitatsBiotopes SpeciesDistribution |
HabitatsBiotopes SeaRegions SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
SeaRegions SpeciesDistribution |
OceanographicFeatures SpeciesDistribution |
OceanographicFeatures SeaRegions SpeciesDistribution |
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Q10c - Access to monitoring data | Q10c Date data are available | 2015-12 |
2014-12 |
2015-04 |
2015-04 |
2015-04 |
2015-10 |
2015-03 |
2015-04 |
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Q10c - Access to monitoring data | Q10c - Data update frequency | Yearly |
3yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
Yearly |
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Q10d - Description of data access | Via OSPAR webpage http://www.mcsuk.org/ospar/ and http://www.ospar.org/content/content.asp?menu=01511400000 |
Previous raw data can be access on request from the data contact at IMARES.
Future raw data will be available from the OSPAR website.
Assessment products available from OSPAR website.
Data will be available at http://bit.ly/1ggNS2E |
In ICES Regional data base (RDB).
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In ICES Regional data base (RDB).
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In ICES Regional data base (RDB).
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A national data base is holding the data.
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ICES is presently working on constructing a database where all aquatic data can be uploaded and stored. Presently DTU Aqua is hosting this database. |
In ICES Regional data base (RDB).
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