Member State report / Art11 / 2020 / D10 / North East Atlantic

Report type Member State report to Commission
MSFD Article Art. 11 Monitoring programmes (and Art. 17 updates)
Report due 2020-10-15
GES Descriptor D10 Litter
Region/subregion North East Atlantic

Member state
BE
DE
DK
ES
FR
IE
NL
PT
SE
Report Access
Descriptor
D10
D10
D10
D10
D10
D10
D10
D10
D10
Monitoring strategy description
The amount of litter in the marine environment is monitored at the seafloor, in the stomach of Northern Fulmars and along the coastline, all in accordance with the OSPAR guidelines. Seafloor litter is collected during beam trawl surveys, while ingested litter is derived from the specimen collected during the beached seabird surveys. The registration of litter types contributes to the identification of the input sources. Evolution over time will show whether progress in achieving GES is made. However, due to changed conditions on the reference beach, a new location had to been chosen and a new time series will be started with regards to litter on the coastline. The suitability of this new beach - Nieuwpoort Lombardsijde - is currently being evaluated.
Eine Beschreibung der gegenwärtigen Belastung und somit eine Abschätzung des Gefährdungspotentials durch Abfälle für die Meeresumwelt der Nordsee ist über die drei gemeinsamen OSPAR-Indikatoren möglich. Sie beinhalten die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste ang...
Marint affald er affald, som stammer fra bevidste og ubevidste handlinger fra erhvervs- og fritidsaktivi-teter på havet eller stranden, eller som tilføres havet via vandløb, spildevand, fra land eller luften. Affald i naturen kan være til gene for dyreliv og mennesker, og tilførslen samt de nuvær...
El Descriptor 10. Basuras marinas, se aborda a través de la estrategia de seguimiento de Basuras Marinas (BM), cuyos objetivos son: • Monitorizar las basuras marinas en los distintos componentes del sistema (playas, fondos marinos, columna de agua y biota) obteniendo información tanto de abundanc...
Le programme de surveillance « Déchets marins » définit la surveillance nécessaire à l'évaluation permanente de l'état écologique des eaux marines et à la mise à jour périodique des objectifs environnementaux (OE) au titre du descripteur 10 « Déchets marins ». Ce programme a pour objectif d'acqué...
Ireland’s marine litter monitoring programme aims to identify the quantity and type of marine litter on Ireland’s coastline and on the seabed. This information allows us to ascertain the pressure that marine litter is causing on our environment, while at the same time determining if measures aimed at reducing marine litter are successful. The monitoring protocols used by Ireland, for both beach litter and seabed litter, have been harmonised at an OSPAR and European Level and were already operational during the first cycle of the MSFD.
The principal purpose of the MSFD monitoring programme is to review the progress that has been made towards achieving good environmental status prescribed for each criterion in the Marine Strategy Part I (2018). This review is based on established indicators. The monitoring can also be used to evaluate the environmental targets defined for each descriptor. The environmental targets are operational in nature and are linked to specific actions and/or measures in the Marine Strategy Part 3. The effects of individual measures cannot generally be linked directly to environmental status or the criteria. Monitoring data can, however, indirectly give an indication of the effectiveness of measures. The monitoring (methods, spatial and temporal coverage) aims to achieve sufficient statistical confidence in the assessment. The risk of not achieving GES or deterioration from GES is addressed in the Marine Strategy, Parts 1 and 3. The European Commission requests that the electronic reports explain how the DPSIR cycle is monitored and to which part of the cycle the monitoring surveys are linked. The MSFD monitoring programme helps to generate better insight into the relationships between the use of the sea and the marine ecosystem. This can be accomplished by monitoring pressures and the underlying activities (D1C1: incidental bycatch, D2: non-indigenous species, D3C1: fish mortality, D5: eutrophication, D6C1/D6C4: physical loss of seabed/habitats and D6C2: fisheries intensity and sand extraction, D8 and D9: pollutants, D10: litter, D11: underwater noise), and by monitoring species and habitats (D1: biodiversity (with the exception of D1C1), D3C2: spawning stock biomass, D4: food web, D6C3/D6C5: habitats ) and hydrographical characteristics (D7). The numerous relationships between the various elements of the marine ecosystem are complex, and many are still not known. Consequently, it is often only possible to give an indication of the impact of specific activities on the marine ecosystem. Experts generally derive DPSIR relationships from the monitoring of pressures/activities and of species and habitats (from the MSFD monitoring programme), in combination with data derived from permits and research programmes. However, some surveys have been established to measure pressures and their effects and/or to learn more about the effectiveness of measures. In designing the monitoring survey for benthic animals (habitats), the Netherlands explicitly took account of the need to
A avaliação do Descritor 10, no Segundo ciclo DQEM, possibilitou a determinação de tendências para algumas categorias de macro-lixo (critério D10C1) para as subdivisões do Continente e Açores. No entanto, não foi possível determinar o Bom Estado Ambiental (BEA) das águas nacionais por insuficiênc...
"By monitoring the ammount of litter on beaches and on the seabed, we can follow trends in quantities and types of marine litter. Such knowledge can form the basis for measures such as preventive measures to reduce the spread of litter or targeted and increased cleaning measures to remove litter from the environment. At present, only macrolitter (> 2.5 cm) is monitored on an regular basis, but monitoring of microlitter (<5 mm) is under development. Mesolitter (5 mm - 2.5 cm) is included to some extent in the monitoring of macro debris. Monitoring of marine litter on beaches and the seabed helps to assess the progress with the relevant target and measures, since the target has indicators backed up with data and the measures are specifically targeting littering. Target E.1 can however be assessed better depending on the ongoing development of monitoring of microlitter. Monitoring of beach litter covers the entire coast of Sweden, albeit sparsely on certain stretches of the coast, and includes different types of beaches to represent Sweden's varying coast. Some beaches are visited by bathers during the summer, while others are less affected if there are no beach visitors. On the West Coast, a lot of litter is washed up from the sea, because currents from the North Sea and in the Skagerrak bring with them litter that has been released in other countries and which is eventually washed up on the West Coast's shores. In the Baltic Sea, on the other hand, smaller amounts of litter are washed up from the sea, so there the litter from visitors is more visible. Within the EU's working group for marine litter, work is underway to try to link litter items to sources/activities more clearly in order to be able to better implement measures where they are needed, but also to be able to follow up if the measures implemented have any effects on what is found in the marine environment. Monitoring of microlitter is under development in Sweden, as regionally agreed methods for sampling and analysis are still in development. However, Sweden carries out monitoring projects with the aim of testing and developing methods for monitoring in different environments and different matrices. Swedish experts also participate in international expert meetings where methods for monitoring and assessing permits are tested and discussed. OSPAR is in the process of developing an indicator for microlitter in sediments. Indicators for microlitter are also discussed within HELCOM, including in sed
Coverage of GES criteria
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring is in place by July 2020
Adequate monitoring was in place in 2014
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Gaps and plans
A project is ongoing to establish a monitoring plan and methodological protocol for the amount of microlitter in the water column and seabed sediment. A baseline for micro-litter in water and sediment as well as in biota for the Belgian part of the North Sea, will become available. The elaboration of a monitoring programme that will gather knowledge on the composition, amount and geographical distribution of microplastics on the long term is needed. Budget request for this monitoring programme is foreseen, the programme is thus dependent upon budget availability and approval.
Nur ein Teil der Belastungen der Meeresumwelt durch Abfälle im Meer wird von den laufenden Monitoringprogrammen erfasst. Mit Ausnahme der genannten Größenfraktion bei Müll im Mägen von Eissturmvogeln, werden die Zusammensetzung, die Menge und die räumliche Verteilung von Mikroabfällen (Bereich un...
Overvågningsprogrammet er tilstrækkeligt. Det skal dog bemærkes hvad angår mikroaffald sediment og vandsøjle, at teknologi og metode stadig er under udvikling.
Descripción de las carencias de la puesta en marcha de los PdS y el plan para completar su establecimiento. Criterio D10C1 (primario): la puesta en marcha de los PdS BM1, BM2, BM3 y BM7 permitirán cubrir adecuadamente el seguimiento de la composición, cantidad y distribución espaci...
Principales perspectives du programme de surveillance « Déchets marins »: - Poursuivre la mise en place de la surveillance des macro-déchets sur le littoral et mettre en œuvre une surveillance des macro-déchets issus des bassins hydrographiques et des micro-déchets dans les sédiments littoraux. A...
Harm Knowledge gaps exist in relation to harm caused by marine litter (both to ecosystems and in socioeconomic terms). Further co-ordinated research is necessary in this area to set refined and justifiable threshold values for marine litter. New models and experimental research is needed to determine whether marine biota populations are declining because of litter and, if so, which parts of the life cycle are affected. At this time, it remains necessary to rely upon the precautionary principle. Surface of the Water Column There is no reliable data at this time in relation to marine litter items on the surface of the water column. Efficient, robust and cost effective monitoring techniques need to be developed for such monitoring to an agreed standard that can be agreed with other EU Member States and, ideally, Contracting Parties to the OSPAR Regional Seas Convention would agree the same monitoring protocols as this is aspect of the marine environment has particular transboundary impact by its nature. Seabed Litter Work is ongoing at TGML to develop a harmonised seabed litter indicator. At this time, survey data is not being gathered in a uniform manner and the existing data sets do not provide a sufficient level of statistical confidence to be able to determine trends.
The IBTS survey, which is primarily established to monitor fish stocks, gives an initial impression of the quantity of litter on the seabed. However, its efficiency in ‘catching’ litter on the seabed is low; the actual quantities are therefore significantly larger than reported. The combined data on litter on the seabed from different North Sea countries are also inadequate for quantitative analysis, but that comparison can be made with a presence/absence analysis. The MSFD monitoring programme will continue to anticipate any further requirements and developments, for example arising from OSPAR or new legislation. OSPAR collaborates closely with the EU Technical Group Marine Litter (TGML). E.g., both groups will investigate how representative the monitoring is for seabed and floating macro litter. Steps are also being taken to improve the quality assurance and quality control of the monitoring. There is no monitoring in place for micro-litter yet, but a new survey for micro-litter in sediment is expected to be launched at the beginning of 2021.
Os programas de monitorização definidos vão permitir acompanhar, para as três subdivisões marinhas, a evolução dos critérios primários D10C1 e D10C2, nos três compartimentos do ambiente marinho: orla costeira, fundos marinhos e camada superficial da coluna de água. Complementarmente, um programa ...
"The monitoring of litter on beaches and seabed provides enough data for assessing D10C1, but the geographical coverage of the monitoring of litter on seabed is partly deficient. Bottom litter is monitored only in connection with the monitoring of demersal fish within the programs IBTS (International bottom trawl survey) in the North Sea, and BITS (Baltic international trawl survey) in the Baltic Sea. In the Baltic Sea, the BITS survey area only covers the Baltic Proper, so the Gulf of Bothnia lacks monitoring. It is being discussed within Helcom whether Finland and Sweden will cover this with a supplementary monitoring in the Gulf of Bothnia. The only problem is that bottom trawling in the shallower areas is not suitable, and the introduction of another method (for example drop video) would not give comparable results with those obtained with BITS. However, as it is necessary to also follow time trends for litter concentrations in areas that should not or cannot be trawled, it is a monitoring that is being considered despite the real need for a different type of sampling methodology. During the 2020 monitoring of hazardous substances in sediments, samples were also collected with the aim of analyzing microlitter. Depending on the results, the Swedish Environmental Protection Agency will investigate the possibilities of including microlitter in the ongoing monitoring of hazardous substances in sediments. In Sweden, it is currently not considered to be a major problem with impacts of litter on animals. Research is underway to investigate the possible effects of litter and microlitter on marine animals, but so far no significant effects that could justify ongoing monitoring have been identified. "
Related targets
  • D10.T1
  • D10.T2
  • D10.T3
  • D10.T4
  • UZN5
  • UZN5.1
  • UZN5.2
  • UZN5.3
  • B.C.10
  • B.C.15
  • B.C.3
  • B.C.4
  • B.C.6
  • B.C.7
  • B.C.8
  • B.C.9
  • B.E.10
  • B.E.11
  • B.E.12
  • B.E.13
  • B.E.18
  • B.E.3
  • B.E.4
  • B.E.5
  • B.E.7
  • B.E.8
  • B.E.9
  • B.L.10
  • B.L.11
  • B.L.12
  • B.L.18
  • B.L.3
  • B.L.4
  • B.L.5
  • B.L.7
  • B.L.8
  • B.L.9
  • B.N.10
  • B.N.11
  • B.N.16
  • B.N.3
  • B.N.4
  • B.N.5
  • B.N.7
  • B.N.8
  • B.N.9
  • B.S.10
  • B.S.11
  • B.S.16
  • B.S.3
  • B.S.4
  • B.S.5
  • B.S.7
  • B.S.8
  • B.S.9
  • C.C.20
  • C.E.16
  • C.L.16
  • C.N.16
  • C.S.16
  • D10-OE01
  • D10-OE02
  • D10T1a
  • D10T1b
  • ANSNL-D10T1
  • ABIPT-T1-D10Cont
  • ABIPT-T2-D10Cont
  • ABIPT-T3-D10Cont
  • AMAPT-T004-D10MAD
  • AMAPT-T007-D10MAD
  • AMAPT-T008-D10MAD
  • AMAPT-T009-D10MAD
  • AMAPT-T010-D10MAD
  • D10-AZO-M1
  • D10-AZO-M2
  • D10-AZO-M3
  • Meta-AZO16
  • ANSSE-E.1_Skräp
  • BALSE-E.1_Skräp
Coverage of targets
Adequate monitoring was in place in 2014
Adequate monitoring will be in place by 2024
Adequate monitoring is in place by July 2020
Adequate monitoring was in place in 2014
Adequate monitoring will be in place by 2024
Adequate monitoring was in place in 2014
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Related measures
  • 1 - 'Report on Environmental Impacts (REI) and Adapted Evaluation (AE)'
  • 15 - 'Measures associated with the land (policies and Directives): Waste Directive, Water Framework Directive, Urban Wastewater Directive, Packaging Framework Directive, policy plan of the Flemish region, policy on waste from coastal municipalities'
  • 16 - 'Land-related measures (raising awareness): awareness campaigns of the OVAM, Clean Beach actions'
  • 19A - 'Installation of port reception facilities(waste collection MARPOL Annex I and V)'
  • 19B - 'Waste management plans for harbours'
  • 21 - 'Monitoring of marine litter conference OSPAR (also considered within the follow-up programme of the MSFD)'
  • 22 - 'Fishing for litter'
  • 28B - 'Raising awareness about waste management in marinas'
  • 29A - 'Improving the system and regulation of waste release from fishing ships'
  • 29B - 'Studying and raising awareness about recycling, deposit, tagging of fishing nets'
  • 29C - 'Study and promotion of alternatives to 'dolly ropes''
  • ANSDE-M004-WFD - 'Bau und Erweiterung Abwasserbehandlungsanlagen / Weitergehende Abwasserbehandlung : Ausbau kommunaler Kläranlagen zur Reduzierung sonstiger Stoffeinträge'
  • ANSDE-M405-UZ2-01 - 'Kriterien und Anreizsysteme für umweltfreundliche Schiffe'
  • ANSDE-M416-UZ5-01 - 'Verankerung des Themas Meeresmüll in Lehrzielen, Lehrplänen und -material'
  • ANSDE-M417-UZ5-02 - 'Modifikation / Substitution von Produkten unter Berücksichtigung einer ökobilanzierten Gesamtbetrachtung'
  • ANSDE-M418-UZ5-03 - 'Vermeidung des Einsatzes von primären Mikroplastikpartikeln'
  • ANSDE-M419-UZ5-04 - 'Reduktion der Einträge von Kunststoffmüll, z.B. Plastikverpackungen, in die Meeresumwelt'
  • ANSDE-M420-UZ5-05 - 'Müllbezogene Maßnahmen zu Fischereinetzen und -geräten'
  • ANSDE-M421-UZ5-06 - 'Etablierung des "Fishing-for-Litter"-Konzepts'
  • ANSDE-M422-UZ5-07 - 'Reduzierung bereits vorhandenen Mülls im Meer'
  • ANSDE-M423-UZ5-08 - 'Reduzierung des Plastikaufkommens durch kommunale Vorgaben'
  • ANSDE-M424-UZ5-09 - 'Reduzierung der Emission und des Eintrags von Mikroplastikpartikeln'
  • ANSDE-M930-other - 'Abfallwirtschaft (Pfandsysteme und Verwertungsquoten für Verpackungen, Deponieverbot für Kunststoffe, Abfallvermeidung)'
  • ANSDE-M931-other - 'Verbot der Einbringung von Abfällen in die Hohe See'
  • ANSDE-M932-other - 'Vorgaben für Hafenauffangeinrichtungen, Mülltagebücher und Müllbehandlungspläne'
  • ANSDE-M933-other - 'Schiffsabfallregelungen: Hafenstaatkontrolle, Sondergebiete nach MARPOL Anlage V'
  • BM1 - 'Implementation of a fixed charging system in ports, similar to that regulated in Royal Legislative Decree 2/2011'
  • BM10 - 'Implementation of the measures contained in the standard transposing Directive 2015/720, amending Directive 94/62 / EC with regard to the reduction of consumption of lightweight plastic bags'
  • BM11 - 'Study on the quantities of marine litter (including microplastics) from waste water treatment plants and proposed specific measures to be incorporated in the basin plans (3rd cycle)'
  • BM12 - 'Ensure the inclusion of explicit references to marine litter in all waste management instruments promoted in the future'
  • BM13 - 'Research into ecological aspects of microplastics'
  • BM14 - 'Study on the quantification of microplastics and identification of possible measures to reduce at source'
  • BM17 - 'Development of a framework document for the development of a coherent scheme of ‘garbage fishing’'
  • BM18 - 'Promotion and financing of garbage ‘fishing activities’'
  • BM19 - 'Financing cleaning activities for rivers, beaches, floating litter and shallow seabeds'
  • BM20 - 'Promoting and coordinating marine litter clean-ups as a citizens’ awareness tool'
  • BM21 - 'Study of marine litter hotspots (zones of major accumulation or zones that are particularly vulnerable to marine litter)'
  • BM22 - 'Cleaning campaigns directed at identified hotspots for marine litter'
  • BM23 - 'Development of a protocol of action on lost or abandoned fishing gear representing a threat to habitats and species’ conservation in Natura 2000 sites'
  • BM24 - 'Preparation of awareness raising/communication materials, with the possibility of a media awareness campaign'
  • BM25 - 'Establish a national technical group on marine litter'
  • BM26 - 'Creating and maintaining a national database of objects recognised as, and activities of, ‘waste fishing’'
  • BM27 - 'Creation of ’Beach Guardian’ roles, aimed at associations, environmental organisations, fishermen’s associations and other collectives, as well as of a network of ‘guardian’ organisations watching over the environmental protection of rivers and beaches and raising awareness about these issues at local, autonomous and national level'
  • BM28 - 'Sizing standards for storm tanks'
  • BM29 - 'Treatment/Disposal at landfill in Melilla of paper and plastic waste (Chafarinas Islands)'
  • BM3 - 'Boosting projects to reduce, reuse and recycle certain materials such as expanded polystyrene (EPS) or fishing nets'
  • BM4 - 'Boosting innovative projects and initiatives on environmental aspects of technologies and processes in the fishing and aquaculture sector'
  • BM5 - 'Promote the installation of clean points in the fishing docks'
  • BM6 - 'Improvement of waste management in ports'
  • BM7 - 'Encouraging projects for better management of waste on board fishing vessels or aquaculture'
  • BM8 - 'Elaboration of regional plans of waste management'
  • BM9 - 'Regulatory review affecting the implementation of the extended responsibility of the producer of the product'
  • CONT12 - 'Drafting of Maritime Inland Plans'
  • CONT5 - 'Regulatory approval of the guidelines for the characterisation of the dredged material and its relocation in waters of the maritime-terrestrial public domain'
  • EMP10 - 'Management and follow-up of the protected spaces (marine reserves)'
  • EMP11 - 'Awareness raising/ dissemination of marine reserves'
  • H1 - 'Regulation of criteria for compatibility with strategies in accordance with Article 3(3) of Law 41/2010'
  • H10 - 'Training programmes designed for fishermen, onboard observers, and staff monitoring stranded animals on coasts, and training for administrative managers'
  • H11 - 'Awareness programmes aimed at beach users and marine tourism companies, as well as the fisheries and agriculture sectors and society in general'
  • H12 - 'Development and implementation of a curriculum related to respect and protection of cetaceans, sea turtles and protected elasmobranches, as well as marine litter, in the official courses of licensed boats of the recreational sector and fishing'
  • H13 - 'Encouraging innovative projects to improve the sustainability of aquaculture facilities'
  • H2 - 'Development of a strategy for visibility and dissemination of the Marine Strategies'
  • H4 - 'Programme for dissemination at schools'
  • H6 - 'Integrated Territorial Investment (ITI) financial tool for the ‘Mar Menor’'
  • ACSIE-M014 - 'Continue to implement the Strategic Environmental Assessment Directive (2001/42/EC) in order to identify, minimise and mitigate potential adverse environmental impacts.'
  • ACSIE-M015 - 'Awareness and training of best practices in maritime and coastal activities and preservation of the marine environment.'
  • ACSIE-M035 - 'Continue to implement Ireland´s Cetacean Conservation Plan.'
  • ACSIE-M066 - 'Apply Environmental Liability Directive (2004/35/EC) as appropriate.'
  • ACSIE-M067 - 'Implementation of Directive 2013/30/EU on safety of offshore oil and gas operations within Irish Legislation. This ensures protection of the marine environment through implementation of safety measures/mechanisms for offshore oil and gas operations. This includes, inter alia, as per Article 8 of Directive 2013/30/EU, the appointment of the Commission of Energy Regulation (CER) as the competent authority responsible for regulatory functions in this regard.'
  • ACSIE-M068 - 'Ensuring on-going implementation of guidelines for the assessment of dredged material for disposal in Irish waters, the application of the Foreshore Acts and the licensing, permitting and enforcement of activities under the Dumping At Sea Act.'
  • ACSIE-M124 - 'Continue to implement national legislation to appropriately apply licensing, regulation and planning for the marine and coastal environment, including the requirement for applications to be accompanied by the materials necessary for a full assessment of the proposed plan, project or development.'
  • ACSIE-M125 - 'Ensure that appropriate forms and levels of organisational governance are in place to support Foreshore Licensing, Petroleum Exploration/Appraisal/ Production Licensing, and proposed Maritime Option Licensing process.'
  • ACSIE-M126 - 'Ensure that the consenting/ permitting processes, overseen by relevant regulatory bodies/statutory bodies, sufficiently account for the adequate protection of habitats and species.'
  • ACSIE-M128 - 'To apply the Environmental Impact Assessment Directive and associated legislation in relation to licences and consents.'
  • ACSIE-M129 - 'Continue to develop and implement river basin and shoreline management plans to control impacts and improve environmental status.'
  • ACSIE-M130 - 'Develop and implement marine plans for all of Irish waters by 31st March 2021 at the latest.'
  • ACSIE-M133 - 'Ensure that environmental monitoring and mitigation measures stipulated in Environmental Impact Statements are fit for purpose and when/where deemed necessary are conducted appropriately.'
  • ACSIE-M148 - 'Continue to control discharges through existing regulation procedures (licensing and permitting of activities) – Integrated Pollution Prevention and Control licences, Waste Water Discharge Licence, Local Authority Wastewater Authorisation (smaller discharges), Local Authority Waste Licences, Agricultural controls, Single Dwelling House Waste Water Systems and the implementation of Pollution Reduction Plans.'
  • ACSIE-M151 - 'Progressively implement the OSPAR Offshore Oil and Gas Industry Strategy.'
  • ACSIE-M156 - 'Implement OSPAR Recommendation 2003/5 promoting the use and implementation of environmental management systems by the offshore industry.'
  • ACSIE-M158 - 'Continue to enforce the Dumping at Sea Act 1996 (as amended), which specifically prohibits the dumping of certain materials at sea and requires any person who wishes to dispose of material at sea to apply to the EPA for a Dumping at Sea permit.'
  • ACSIE-M164 - 'Continued Prevention of Pollution by Garbage from Ships through the implementation of regulations laid out in MARPOL Annex V (entered into force 31 December 1988) and S.I. No. 372/2012'
  • ACSIE-M167 - 'Continued provision of port waste reception facilities in commercial and fishing ports.'
  • ACSIE-M181 - 'To continue to enforce the Litter Pollution Acts 1997 to 2009, which make littering an offence.'
  • ACSIE-M182 - 'To continue to implement regional waste management plans and a national hazardous waste management plan.'
  • ACSIE-M183 - 'To continue to promote the use of packaging substitution.'
  • ACSIE-M184 - 'To continue to provide appropriate infrastructure for proper litter disposal and recycling including signage and bins.'
  • ACSIE-M185 - 'To continue to support initiatives which promote public pride in local amenity/natural beauty or reinforce social norms against littering.'
  • ACSIE-M186 - 'To continue to apply disincentives to litter (e.g. fines).'
  • ACSIE-M187 - 'To continue to implement the OSPAR Regional Action Plan on Marine Litter'
  • ACSIE-M188 - 'To continue to apply Waste Prevention Programmes.'
  • ACSIE-M189 - 'To continue efforts to improve business attitudes and behaviours around marine and coastal litter.'
  • ACSIE-M190 - 'Continue beach cleaning (with Local Authority operational cleaning of the foreshore) and litter enforcement.'
  • ACSIE-M191 - 'To continue to contribute to a low carbon economy by treating “waste as a resource”.'
  • ACSIE-M192 - 'Promote greater reuse and recycling of goods and materials and management of waste.'
  • ACSIE-M193 - 'To continue to charge for single use carrier bags through the applications of the Plastic Bag (Amendment) (No.2) Regulations (S.I. No. 167/2007), amending Plastic Bag Regulations (S.I. No. 605/2001).'
  • ACSIE-M194 - 'To promote the use of the National Environmental Complaints Line and the reporting of environmental pollution, fly-tipping and illegal dumping of waste; including the National Litter Pollution Monitoring System, funded by DECLG'
  • ACSIE-M195 - 'To encourage the reuse and recycling of waste and the reduction of the amount of waste destined for landfill through the application of Waste Management (Landfill Levy) Regulations 2002-2013.'
  • ACSIE-M196 - 'To continue to enforce the requirement to put in place a site waste management plan at marine-related developments through the application of the EU Directive 2000/59/EC on port reception facilities for ship-generated wastes and cargo residues.'
  • ACSIE-M197 - 'Combined Storm Overflow Control (screening & limiting of spills) and application of the discharge licensing requirements set by the Environmental Protection Agency under the Waste Framework Directive and Urban Waste Water Treatment Directive and the Integrated Pollution Prevention and Control Directive.'
  • ACSIE-M198 - 'To reduce litter entering rivers and other water bodies by addressing pollution from surface water runoff and drainage through the application of the Water Framework Directive (2000/60/EC).'
  • ACSIE-M201 - 'Measures to maintain restrictions on the range of material that can be disposed of at sea from ships; and increase and improve port reception facilities for ship-generated waste; and extend port waste reception facilities to fishermen.'
  • ACSIE-M202 - 'To continue to raise awareness to tackle the sources of litter through the Blue Flag Beach and Green Coast Award programmes.'
  • ACSIE-M203 - 'Continue to implement the Producer Responsibility Initiative to increase the recycling of waste electrical and electronic equipment.'
  • ACSIE-M204 - 'Continue to enforce legislation (S.I. No. 513/2012) restricting the use of hazardous substances in electrical and electronic equipment.'
  • ACSIE-M205 - 'To continue to implement the Producer Responsibility Initiative to increase the recycling of farm plastic waste through the application of the farm plastics recovery scheme.'
  • ACSIE-M206 - 'Maintain and expand the Fishing for Litter Scheme.'
  • ACSIE-M207 - 'Continue to promote and support An Taisce´s programme on Ocean Literacy.'
  • ACSIE-M208 - 'Maintain sea users’ awareness of waste issues and encourage compliance with existing rules.'
  • ACSIE-M209 - 'Continue to promote the waste management service in order to provide alternative methods for the disposal of discarded fishing gear.'
  • ACSIE-M212 - 'To continue to apply the BIM Responsibly Sourced Standard for wild capture fisheries.'
  • ACSIE-M213 - 'To continue to raise awareness to tackle the sources of litter through the international environmental education programme Eco-Schools. This includes developing an international Eco-School module on marine litter with the Celtic Seas Partnership, Eco Schools (FEE - Copenhagen) and An Taisce.'
  • ACSIE-M214 - 'On-going implementation of the #2minutebeachclean/#Glantra2noimead initiative and expansion across all blue flag beaches in Ireland.'
  • ACSIE-M215 - 'Continue to implement the Producer Responsibility Initiative to increase the recycling of construction and demolition waste.'
  • ACSIE-M216 - 'Continue to implement the Producer Responsibility Initiative to increase the recycling of construction and demolition waste.'
  • ACSIE-M217 - 'Continue to implement the Producer Responsibility Initiative (PRI) to increase the recycling of packaging waste; and to continue to promote, co-ordinate and finance the collection and recovery of packaging waste in order to achieve the objectives set out in the Packaging Waste Directive.'
  • ACSIE-M218 - 'Continue to implement the Producer Responsibility Initiative to increase the recycling of tyres.'
  • ACSIE-M219 - 'To continue to implement the Producer Responsibility Initiative to increase the recycling of end – of - life vehicles.'
  • ACSIE-M220 - 'Continue to promote the Bord Iascaigh Mhara Environment Management System (EMS) to assist fishermen to implement practices to help minimise the impact of fishing effort on the marine environment.'
  • ACSIE-M221 - 'Continue to promote the implementation of the Environment Management System on fish and shellfish farms through the Environment Management System for Aquaculture initiative.'
  • ANSNL-M024 - '(Schoonmaak)- campagnes'
  • ANSNL-M025 - 'Aanpak Schone Maas Limburg'
  • ANSNL-M026 - 'Initiatief Duurzaam Doen'
  • ANSNL-M027 - 'Stakeholderinitiatieven op stranden'
  • ANSNL-M028 - 'Implementatie EU-richtlijn Havenontvangstvoorzieningen'
  • ANSNL-M029 - 'Lozingsverbod vuilnis door schepen (MARPOL Annex V)'
  • ANSNL-M030 - 'Marine environmental awareness cursus'
  • ANSNL-M031 - 'Programma Fishing for Litter'
  • ANSNL-M032 - 'Uitvoering (zwerf) afvalbeleid'
  • ANSNL-M033 - 'Vrijwillige vermindering van microplastics in cosmetica in Nederland'
  • ANSNL-M053 - 'Van Afval naar Grondstof (VANG)'
  • ANSNL-M054 - 'Raamovereenkomst Verpakkingen 2013-2022'
  • ANSNL-M055 - 'Landelijke aanpak zwerfafval'
  • ANSNL-M056 - 'Ketenakkoord kunststofkringloop'
  • ANSNL-M057 - 'Landelijk Afvalbeheerplan (LAP) 2'
  • ANSNL-M058 - 'Terugdringen van het gebruik van plastic tassen'
  • ANSNL-M062 - 'Agendering zwerfvuil bij stakeholders en in onderwijs'
  • ANSNL-M063 - 'Green Deal Schone Stranden'
  • ANSNL-M064 - 'Agendering bij waterbeheerders'
  • ANSNL-M065 - 'Stroomgebiedsgerichte aanpak zwerfvuil'
  • ANSNL-M066 - 'Uitrol Ophaalregeling zwerfvuil'
  • ANSNL-M067 - 'Green Deal Scheepsafvalketen'
  • ANSNL-M068 - 'Green Deal Visserij voor een schone zee'
  • ANSNL-M069 - 'Bewustwording in de visserijsector'
  • ANSNL-M070 - 'Bevordering van het terugdringen ballonnen'
  • ANSNL-M071 - 'Inzet op EU-verbod op emissies van microplastics in cosmetica en detergenten'
  • ABI-PT-ME02-D10 - 'BDLixLit – Desenvolver uma base de dados sobre lixo marinho no litoral'
  • ABI-PT-ME04-D10 - 'LiMar – Determinar bioindicadores para o lixo marinho'
  • AMA-PT-ME08-DV - 'DQEMsat – Implementar a utilização de imagens de satélite para aquisição de conhecimento sobre o meio marinho'
  • AMA-PT-MEA11-D10 - 'Implementar um programa de gestão de lixo a bordo de embarcações de pesca'
  • AMA-PT-MEMAD08-D10 - 'VEGAS (Vigilante Atlântico das Selvagens) - Avaliar a potencialidade das ilhas Selvagens como espaço de excelência para monitorizar o lixo marinho'
  • ANSSE-M019 - 'ÅPH 19 - Promote efficient and sustainable collection and receipt of lost fishing gear and prevent loss of new gear'
  • ANSSE-M020 - 'ÅPH 20 - Targeted national information campaign about common debris in the marine environment, their negative impact on the environment and the link to consumer behaviour'
  • ANSSE-M021 - 'ÅPH 21 - Supporting initiatives that promote, organise and carry out beach cleaning in badly affected areas'
  • ANSSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • ANSSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
  • ANSSE-M034 - 'National environmental targets'
  • BALSE-M019 - 'ÅPH 19 - Promote efficient and sustainable collection and receipt of lost fishing gear and prevent loss of new gear'
  • BALSE-M020 - 'ÅPH 20 - Targeted national information campaign about common debris in the marine environment, their negative impact on the environment and the link to consumer behaviour'
  • BALSE-M022 - 'ÅPH 22 - Conducting strategic work through the inclusion of marine debris in relevant waste management plans and programmes'
  • BALSE-M023 - 'ÅPH 23 - The revision of the municipal waste management plans needs to identify and illustrate how waste management can help to reduce the occurrence of marine litter and set up goals for such work'
Coverage of measures
Adequate monitoring was in place in 2014
Adequate monitoring will be in place by 2024
Adequate monitoring is in place by July 2020
Adequate monitoring was in place in 2014
Adequate monitoring was in place in 2014
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Adequate monitoring will be in place by 2024
Related monitoring programmes
  • ANSBE-P25-Litter-1-beach
  • ANSBE-P26-Litter-2-seafloor
  • ANSBE-P27-Litter-3-Ingested
  • ANSDE_MPr_020_MP_051
  • ANSDE_MPr_020_MP_066
  • ANSDE_MPr_020_MP_067
  • ANSDE_MPr_020_MP_068
  • ANSDE_MPr_020_MP_071
  • ANSDE_MPr_020_MP_073
  • ANSDE_MPr_020_MP_262
  • ANSDE_MPr_022_MP_070
  • DK-D10-01
  • DK-D10-02
  • DK-D10-03
  • DK-D10-04
  • DK-D10-05
  • DK-D10-06
  • DK-D10-07
  • ES-BM-1_BasuraPlayas
  • ES-BM-2_BasuraFlotante
  • ES-BM-3_BasuraFondoMarino
  • ES-BM-4_MicroplásticosAgua
  • ES-BM-5_MicroplásticosFondo
  • ES-BM-6_MicroplasticosPlayas
  • ES-BM-7_DatosAdicionales
  • ES-BM-8_BasurasBiota
  • ES-OA-B
  • ES-PSBE-04_AporteBasuras
  • FR-ABI-D10-01
  • FR-ABI-D10-04
  • FR-ABI-D10-05
  • FR-ABI-D10-06
  • FR-ABI-D10-08
  • FR-ABI-D10-09
  • FR-ABI-D10-10
  • FR-ACS-D10-01
  • FR-ACS-D10-04
  • FR-ACS-D10-05
  • FR-ACS-D10-06
  • FR-ACS-D10-08
  • FR-ACS-D10-09
  • FR-ACS-D10-10
  • FR-ANS-D10-01
  • FR-ANS-D10-04
  • FR-ANS-D10-05
  • FR-ANS-D10-06
  • FR-ANS-D10-07
  • FR-ANS-D10-08
  • FR-ANS-D10-09
  • FR-ANS-D10-10
  • ACS-IE-D03-01
  • ACS-IE-D10-01
  • ANSNL-D10-Sub1-OSPAR-Beach
  • ANSNL-D10-Sub2-OSPAR-Fulmar
  • ANSNL-D10-Sub2-OSPAR-FulmarC3
  • ANSNL-D10-Sub2-OSPAR-seabed
  • ANSNL-D10-microafval
  • PT-AMA-MO-D10-MacroWC
  • PT-AZO-MO-COSTA
  • PT-AZO-MO-MONICO
  • PT-CONT-MO-D10-Portos
  • PT-MO-D10-B
  • PT-MO-D10-MacroC
  • PT-MO-D10-MacroSB
  • PT-MO-D10-MicroC
  • PT-MO-D10-MicroWC-SB
  • SE-D10-beachlitter
  • SE-D10-microlitter
  • SE-D10-seabedlitter
Programme code
ANSBE-P25-Litter-1-beach
ANSBE-P26-Litter-2-seafloor
ANSBE-P27-Litter-3-Ingested
ANSDE_MPr_020_MP_051
ANSDE_MPr_020_MP_066
ANSDE_MPr_020_MP_067
ANSDE_MPr_020_MP_068
ANSDE_MPr_020_MP_071
ANSDE_MPr_020_MP_073
ANSDE_MPr_020_MP_262
ANSDE_MPr_022_MP_070
DK-D10-01
DK-D10-02
DK-D10-03
DK-D10-04
DK-D10-05
DK-D10-06
DK-D10-07
ES-BM-1_BasuraPlayas
ES-BM-2_BasuraFlotante
ES-BM-3_BasuraFondoMarino
ES-BM-4_MicroplásticosAgua
ES-BM-5_MicroplásticosFondo
ES-BM-6_MicroplasticosPlayas
ES-BM-7_DatosAdicionales
ES-BM-8_BasurasBiota
ES-OA-B
ES-PSBE-04_AporteBasuras
FR-ABI-D10-01
FR-ABI-D10-04
FR-ABI-D10-05
FR-ABI-D10-06
FR-ABI-D10-08
FR-ABI-D10-09
FR-ABI-D10-10
FR-ACS-D10-01
FR-ACS-D10-04
FR-ACS-D10-05
FR-ACS-D10-06
FR-ACS-D10-08
FR-ACS-D10-09
FR-ACS-D10-10
FR-ANS-D10-01
FR-ANS-D10-04
FR-ANS-D10-05
FR-ANS-D10-06
FR-ANS-D10-07
FR-ANS-D10-08
FR-ANS-D10-09
FR-ANS-D10-10
ACS-IE-D03-01
ACS-IE-D10-01
ANSNL-D10-Sub1-OSPAR-Beach
ANSNL-D10-Sub2-OSPAR-Fulmar
ANSNL-D10-Sub2-OSPAR-FulmarC3
ANSNL-D10-Sub2-OSPAR-seabed
ANSNL-D10-microafval
PT-AMA-MO-D10-MacroWC
PT-AZO-MO-COSTA
PT-AZO-MO-MONICO
PT-CONT-MO-D10-Portos
PT-MO-D10-B
PT-MO-D10-MacroC
PT-MO-D10-MacroSB
PT-MO-D10-MicroC
PT-MO-D10-MicroWC-SB
SE-D10-beachlitter
SE-D10-microlitter
SE-D10-seabedlitter
Programme name
Beach litter monitoring
Seafloor litter
Monitoring plastics in Northern Fulmars
Abfall - Merkmale und Abundanz/Volumen: Erfassung von Abfällen in Mägen von Meeresfischen (Nordsee)
Abfall - Merkmale und Abundanz/Volumen: Erfassung von Strandmüll - Makroabfälle (Nordsee)
Abfall - Merkmale und Abundanz/Volumen: Erfassung von Kunststoffen in Mägen von Eissturmvögeln (Nordsee)
Abfall - Merkmale und Abundanz/Volumen: Erfassung von Abfällen auf dem Meeresboden (Nordsee)
Abfall - Merkmale und Abundanz/Volumen: Meeresmüll als Nistmaterial in Brutkolonien von Vögeln und assoziierte Mortalitäten infolge Verstrickung
Abfall - Merkmale und Abundanz/Volumen: Erfassung von Abfällen an der Wasseroberfläche (Nordsee)
Abfall - Merkmale und Abundanz/Volumen: Erfassung von Paraffinen und anderen "Persistent Floatern" (Nordsee)
Abfall Mikropartikel - Abundanz/Volumen: Erfassung von Mikropartikeln (< 5 mm) in Wasser und Sediment (Nordsee)
Litter/micro-litter in biota - fulmars
Litter/micro-litter in biota - other species
Litter - characteristics and abundance/volume on coast
Litter - characteristics and abundance/volume on seabed - trawl survey
Litter - characteristics and abundance on seabed - lost fishing gear
Litter micro-particles - abundance in sediment
Litter micro-particles - abundance in water
Basura en playas
Basura flotante
Basura en el fondo marino
Microplásticos en aguas superficiales
Microplásticos en el fondo marino
Microplásticos en playas
Ciencia ciudadana
Basuras en biota
Objetivos ambientales sobre vertidos al medio marino (B)
Aporte de basuras
Macro-déchets sur le littoral
Macro-déchets flottants
Macro-déchets sur le fond
Micro-déchets flottants
Déchets ingérés par les mammifères marins et les tortues marines
Emmêlement/ Enchevêtrement de la faune par les déchets
Partie activités, usages et politiques publiques
Macro-déchets sur le littoral
Macro-déchets flottants
Macro-déchets sur le fond
Micro-déchets flottants
Déchets ingérés par les mammifères marins et les tortues marines
Emmêlement/ Enchevêtrement de la faune par les déchets
Partie activités, usages et politiques publiques
Macro-déchets sur le littoral
Macro-déchets flottants
Macro-déchets sur le fond
Micro-déchets flottants
Déchets ingérés par les oiseaux
Déchets ingérés par les mammifères marins et les tortues marines
Emmêlement/ Enchevêtrement de la faune par les déchets
Partie activités, usages et politiques publiques
Irish Groundfish Survey - Litter
OSPAR Beach Litter Monitoring Programme
Litter - characteristics and abundance/volume on coast, water surface, seabed
Litter - characteristics and abundance/volume on coast, water surface, seabed
Litter/micro-litter in biota
Litter - characteristics and abundance/volume on coast, water surface, seabed
Litter micro-particles - abundance/volume in water, sediment
Monitorização de macrolixo na superfície do mar
Projeto COSTA - Programa de observação para a pesca com palangre de superfície nos Açores
MONICO- Programa de Monitorização de Recursos e Ambientes Costeiros dos Açores
Monitorização de lixo marinho nas áreas de jurisdição portuária
Impacto do macrolixo e microlixo na biota
Monitorização de macrolixo na orla costeira/praias
Monitorização de macrolixo nos fundos
Monitorização de microlixo na orla costeira/praias
Monitorização de microlixo nos fundos e na coluna de água
Litter on coast
Litter micro-particles
Litter on seabed
Update type
Modified from 2014
New programme
Modified from 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
New programme
Same programme as in 2014
Modified from 2014
New programme
Same programme as in 2014
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
New programme
New programme
New programme
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
New programme
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
New programme
New programme
New programme
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
New programme
New programme
New programme
Modified from 2014
Modified from 2014
Modified from 2014
Modified from 2014
New programme
New programme
New programme
New programme
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
Same programme as in 2014
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
New programme
Modified from 2014
New programme
Modified from 2014
Old programme codes
  • ANSBE-D10-Litter-SP26
  • ANSBE-D10-Litter-SP28
  • ANSDE_Sub_020
  • ANSDE_Sub_020
  • ANSDE_Sub_020
  • ANSDE_Sub_020
  • ANSDE_Sub_020
  • ANSDE_Sub_020
  • ANSDE_Sub_020
  • ANSDE_Sub_022
  • ANSDK-D10-05_LITTER_fulmars
  • BALDK-D10-03_litter_microplastic
  • ANSDK-D10-04_LITTER_beach
  • ANSDK-D10-02-LITTER_seafloor
  • BALDK-D10-02_litter_seafloor
  • ABIES-NOR-BM-1_OSPAR_BasurasPlayas
  • ABIES-SUD-BM-1_OSPAR_BasurasPlayas
  • AMAES-CAN-BM-1_BasurasPlayas
  • MWEES-ESAL-BM-1_BasurasPlayas
  • MWEES-LEBA-BM-1_BasurasPlayas
  • ABIES-NOR-BM-2_BasuraFlotante
  • ABIES-SUD-BM-2_BasuraFlotante
  • AMAES-CAN-BM-2_BasuraFlotante
  • MWEES‐ESAL‐ BM-2_BasuraFlotante
  • MWEES‐LEBA‐BM-2_BasuraFlotante
  • ABIES-NOR-BM-3_BasuraFondoMarino
  • ABIES-SUD-BM-3_BasuraFondoMarino
  • AMAES-CAN- BM-3_BasuraFondoMarino
  • MWEES‐ESAL‐BM-3_BasuraFondoMarino
  • MWEES‐LEBA‐BM-3_BasuraFondoMarino
  • ABIES-NOR-BM-4_MicroparticulasAgua
  • ABIES-SUD-BM-4_MicroparticulasAgua
  • AMAES-CAN-BM-4_MicroparticulasAgua
  • MWEES‐ESAL‐ BM-4_MicroparticulasAgua
  • MWEES‐LEBA‐BM-4_MicroparticulasAgua
  • ABIES-NOR-BM-5_MicroparticulasFondo
  • ABIES-SUD-BM-5_MicroparticulasFondo
  • AMAES-CAN-BM-5_MicroparticulasFondo
  • MWEES-ESAL-BM-5_MicroparticulasFondo
  • MWEES‐LEBA‐BM-5_MicroparticulasFondo
  • ABIES-NOR-BM-6_MicroplasticosPlayas
  • ABIES-SUD-BM-6_MicroplasticosPlayas
  • AMAES-CAN-BM-6_MicroplasticosPlayas
  • MWEES-ESAL-BM-6_MicroplasticosPlayas
  • MWEES-LEBA-BM-6_MicroplasticosPlayas
  • ABIES-NOR-BM-7_Datos adicionales
  • ABIES-SUD-BM-7_Datos adicionales
  • AMAES-CAN- BM-7_Datos adicionales
  • MWEES‐ESAL‐BM-7_Datos adicionales
  • MWEES‐LEBA‐BM-7_Datos adicionales
  • GDGFR-D10_Dechets-1-Littoral
  • GDGFR-D10_Dechets-2-Flottants
  • GDGFR-D10_Dechets-3-Fond
  • GDGFR-D10_Dechets-4-Microparticules
  • MCFR-D10_Dechets-1-Littoral
  • MCFR-D10_Dechets-2-Flottants
  • MCFR-D10_Dechets-3-Fond
  • MCFR-D10_Dechets-4-Microparticules
  • MMNFR-D10-01_DechetsLittoral
  • MMNFR-D10-02_DechetsFlottants
  • MMNFR-D10-03_DechetsFond
  • MMNFR-D10-04_Microparticules
  • ACS-IE-D03-012
  • ACS-IE-D03-02
  • ACS-IE-D03-04
  • ACS-IE-D03-05
  • ACS-IE-D03-06
  • ACS-IE-D03-07
  • ACS-IE-D03-08
  • ACS-IE-D03-09
  • ACS-IE-D03-10
  • ACS-IE-D03-11
  • ACS-IE-D03-13
  • ACS-IE-D03-14
  • ACS-IE-D03-15
  • ACS-IE-D03-16
  • ACS-IE-D03-17
  • ASC-IE-D03-03
  • ANSSE-Litter-D10-Strand
  • BALSE-Litter-D10-Strand
  • ANSSE-Litter-D10-Botten
  • BALSE-Litter-D10-Botten
Programme description
Belgian reference beaches are searched four times a year (seasonally) for litter items of which the numbers are noted on monitoring sheets with pre-defined categories following the internationally agreed Guideline for Monitoring Marine Litter on the Beaches in the OSPAR maritime area (2010). Since 2017, monitoring of the two reference beaches is not representative anymore due to the high frequency of beach cleaning. Starting from 2020, a new reference beach at Lombardsijde, which is closed for the public, will be monitored and evaluated. This monitoring contributes to the evaluation of the environmental targets D10.1 and D10.2.
This programme aims to monitor litter contamination at the seafloor of the BPNS. Data is collected within the beam trawl survey, see ANSBE-P3-Fish-1-populationfor more details. This programme contributes to environmental target D10.3.
Since 2002 INBO determines the presence of plastics in the stomachs of beached Northern Fulmars. The specimens are collected during monthly wintersurveys of beached seabirds along the entire Belgian coast. Dissection takes place during international workshops organized by IMARES-Texel or in Belgium under the auspices of trained INBO-personnel. INBO also performs the actual analyses of stomach contents. The data will be used to evaluate the environmental target D10.4: Less than 10 % of the northern fulmars (Noordse stormvogel - Fulmarus glacialis) contain more than 0,1 g plastic in their stomach. (Former programme ANSBE-D10-Litter-SP28)
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_51 || Erfassung von Abfällen in Mägen von Meeresfischen (Nordsee) || Die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste angeschwemmt und von Nutzern der Strände dort hinterlassen we...
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_66 || Erfassung von Strandmüll - Makroabfälle (Nordsee) || Die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste angeschwemmt und von Nutzern der Strände dort hinterlassen werden (Stra...
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_67 || Erfassung von Kunststoffen in Mägen von Eissturmvögeln (Nordsee) || Die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste angeschwemmt und von Nutzern der Strände dort hinterlass...
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_68 || Erfassung von Abfällen auf dem Meeresboden (Nordsee) || Die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste angeschwemmt und von Nutzern der Strände dort hinterlassen werden (S...
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_71 || Meeresmüll als Nistmaterial in Brutkolonien von Vögeln und assoziierte Mortalitäten infolge Verstrickung || Die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste angeschwemmt und...
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_73 || Erfassung von Abfällen an der Wasseroberfläche (Nordsee) || Die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste angeschwemmt und von Nutzern der Strände dort hinterlassen werde...
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_262 || Erfassung von Paraffinen und anderen "Persistent Floatern" (Nordsee) || Die Abschätzung der Mengen und Eigenschaften von Abfällen, die an der Küste angeschwemmt und von Nutzern der Strände dort hinte...
Das Monitoring-Programm besteht aus den/dem folgenden Messprogramm/en (=MP): || ANSDE_MP_70 || Erfassung von Mikropartikeln (< 5 mm) in Wasser und Sediment (Nordsee) || Investigatives Monitoring im Rahmen von F&E-Vorhaben. Dies umfasst die Entwicklung eines automatischen Probenahmegerätes für suspendiertes Mikroplastik in Küsten- und Übergangsgewässern.
Mallemukkers indtag af marint affald, overvåges ud fra analyse af maveindholdet i dødfundne mallemukker. Mallemukken er valgt som indikatorart, da den lever på havet og søger føde på vandoverfladen, hvor mindre stykker af marint affald kan forveksles med dens normale føde. Indsamlingen af mallemu...
Mængden af makro- og mikroaffald i maveindholdet hos sild og torsk er blevet undersøgt i den foregående overvågningsperiode. Det bliver i den kommende programperiode undersøgt om det er fordelagtigt at bruge andre indikator-organismer end sild og torsk eller evt. inddrage tilfældige forekomster (...
Marint affald udgør blandt andet pga. strømmæssige forhold især et problem på strandene langs den jyske vestkyst. Andre faktorer som også spiller ind til problemet er et højt aktivitetsniveau fra bl.a. skibstrafik og fiskeri, udledning af spilde- og overfladevand fra europæiske floder til Nordsøe...
DTU Aqua gennemfører monitering af affald på havbunden forbindelse med forsøgsfiskeri under IBTS og BITS programmerne, som koordineres af ICES. Der er årligt i alt 4 togter med henholdsvis 2 togter i Nordsø/Skagerrak og 2 togter i Østersøen.
Registreringen af tabte fiskeredskaber gennemføres under Fiskeristyrelsens fiskerikontrolkontor. Resultaterne bliver opgjort løbende i overvågnings perioden.
Forekomsten af mikroaffald i sedimenter blev i 2015 undersøgt på ti stationer i den danske del af Nordsøen. Men en systematisk indsamling og analysering af mængden og sammensætningen af mikroaffald i sedimenter er en nystartet overvågning, og er derfor kun foretaget en enkelt gang på fire udvalgt...
Systematisk indsamling og analysering af mængden og sammensætningen af mikroaffald i vandsøjlens overfladelag er en nystartet aktivitet. Prøverne er hidtil indsamlet via en Ferrybox monteret på en færge sejlende igennem Kattegat og Skagerrak. Mikroaffaldet fra de indsamlede vandprøver inddeles i ...
El programa se encarga de estudiar la evolución de las macro-basuras en las playas españolas, incluyendo su abundancia, composición y origen. La toma de datos consiste en la realización de muestreos estacionales (invierno, primavera, verano y otoño) en 26 playas de referencia siguiendo un protoco...
Las basuras flotantes juegan un papel crucial en el ciclo de la basura marina, en este apartado se consideran únicamente las basuras de tamaño mayor a 0,5 mm, ya que piezas de menor tamaño se consideran dentro del indicador microbasuras. De manera experimen...
The programme aims to monitor litter accumulated on the seabed, including its abundance, composition and origin. Seabed areas can be areas of accumulation of marine litter depending on bottom accidents, platform currents, discharge of rivers, close to navigation routes, ports or population centre...
La importancia relativa que tiene la creación de microplásticos como producto de degradación de plásticos de mayor tamaño con respecto a los microplásticos de origen primario (con entrada directa en el medio marino) no se conoce. Las condiciones oceanográficas y las características de los plástic...
This programme, which aims to monitor microparticles in the seabed, is under development, not only in Spain, but also at European level. The lack of standardised means to study this aspect is a weakness in the implementation of marine strategies. Spain is working to address this problem, in coope...
Los microplásticos presentes en las playas pueden producir efectos nocivos sobre la fauna asociada a las mismas (afección sobre el sistema inmunológico, hormonal, etc), pero sobre todo son un indicador de la cantidad de basura existente en el medio marino. Por lo general, la macrobasura proviene ...
La ciencia ciudadana implica la participación del público en general en las actividades de investigación científica en que los ciudadanos contribuyan activamente a la ciencia, ya sea con su esfuerzo intelectual o conocimiento o con sus herramientas y recursos (Comisión Europea, 2014). La sociedad...
Existen varias redes de atención a los varamientos de cetáceos y reptiles en España llevadas a cabo y mantenidas por las administraciones autonómicas
Mediante la Resolución de 11 de junio de 2019 de la Secretaría de Estado de Medio Ambiente, se publicó el Acuerdo del Consejo de Ministros de 7 de junio de 2019, por el que se aprueban los objetivos ambientales del segundo ciclo de las estrategias marinas españolas. Estos objetivos ambientales se...
Se tratará de evaluar el aporte de basuras al medio marino teniendo en cuenta los siguientes aspectos: • la presencia de macrobasuras en playas, • los residuos recogidos en las instalaciones de recepción portuarias de los puertos de interés general, considerando las cantidades recogidas como cantidades de basuras que se ha evitado que lleguen al medio marino.
Ce programme permet de suivre l'évolution de la composition, la quantité et la répartition spatiale des macro-déchets déposés sur le littoral, afin de mieux évaluer la pression par les déchets, de déterminer la répartition spatiale et cibler les activités humaines à l'origine de ces déchets. La s...
Ce programme permet de suivre l'évolution de la composition et de la quantité des macro-déchets qui flottent à la surface de la mer, ainsi que leur répartition spatiale. Elle repose principalement sur des observateurs embarqués à bord de navires ou à bord de campagnes aériennes, comptabilisant à ...
Ce programme permet de suivre l'évolution de la composition, la quantité et de la répartition spatiale, des macro-déchets présents sur les fonds marins. Ce sous-programme repose aujourd'hui sur le dispositif des campagnes halieutiques DCF optimisées - déchets de fond, notamment les campagnes bent...
Ce programme permet de suivre l'évolution de la composition, de la quantité et de la répartition spatiale des micro-déchets (300 µm – 5mm) présents en sub-surface. Ce sous-programme repose sur le dispositif de surveillance « Campagnes halieutiques DCF optimisées – Micro-déchets » qui consiste en ...
Ce programme permet de suivre la nature et la quantité de déchets ingérés par les tortues marines et dans une moindre mesure par les mammifères marins retrouvés échoués sur le littoral. Il repose principalement sur le dispositif de surveillance « Réseaux de suivi des échouages des tortues marines...
Ce programme permet de suivre l'emmêlement et l'enchevêtrement de la faune marine (oiseaux marins, mammifères marins, tortues marines, faune épibenthique) par les déchets marins. Le suivi de l'emmêlement et enchevêtrement des oiseaux marins repose sur le dispositif de surveillance « Suivi des mac...
En France, la DCSMM est mise en œuvre conjointement avec la directive 2014/89/UE (établissant un cadre pour la planification de l'espace maritime) à travers les documents stratégiques de façade. Dans cette démarche, le document stratégique de façade contribue à améliorer la prise en compte récipr...
Ce programme permet de suivre l'évolution de la composition, la quantité et la répartition spatiale des macro-déchets déposés sur le littoral, afin de mieux évaluer la pression par les déchets, de déterminer la répartition spatiale et cibler les activités humaines à l'origine de ces déchets. La s...
Ce programme permet de suivre l'évolution de la composition et de la quantité des macro-déchets qui flottent à la surface de la mer, ainsi que leur répartition spatiale. Elle repose principalement sur des observateurs embarqués à bord de navires ou à bord de campagnes aériennes, comptabilisant à ...
Ce programme permet de suivre l'évolution de la composition, la quantité et de la répartition spatiale, des macro-déchets présents sur les fonds marins. Ce sous-programme repose aujourd'hui sur le dispositif des campagnes halieutiques DCF optimisées - déchets de fond, notamment les campagnes bent...
Ce programme permet de suivre l'évolution de la composition, de la quantité et de la répartition spatiale des micro-déchets (300 µm – 5mm) présents en sub-surface. Ce sous-programme repose sur le dispositif de surveillance « Campagnes halieutiques DCF optimisées – Micro-déchets » qui consiste en ...
Ce programme permet de suivre la nature et la quantité de déchets ingérés par les tortues marines et dans une moindre mesure par les mammifères marins retrouvés échoués sur le littoral. Il repose principalement sur le dispositif de surveillance « Réseaux de suivi des échouages des tortues marines...
Ce programme permet de suivre l'emmêlement et l'enchevêtrement de la faune marine (oiseaux marins, mammifères marins, tortues marines, faune épibenthique) par les déchets marins. Le suivi de l'emmêlement et enchevêtrement des oiseaux marins repose sur le dispositif de surveillance « Suivi des mac...
En France, la DCSMM est mise en œuvre conjointement avec la directive 2014/89/UE (établissant un cadre pour la planification de l'espace maritime) à travers les documents stratégiques de façade. Dans cette démarche, le document stratégique de façade contribue à améliorer la prise en compte récipr...
Ce programme permet de suivre l'évolution de la composition, la quantité et la répartition spatiale des macro-déchets déposés sur le littoral, afin de mieux évaluer la pression par les déchets, de déterminer la répartition spatiale et cibler les activités humaines à l'origine de ces déchets. La s...
Ce programme permet de suivre l'évolution de la composition et de la quantité des macro-déchets qui flottent à la surface de la mer, ainsi que leur répartition spatiale. Elle repose principalement sur des observateurs embarqués à bord de navires ou à bord de campagnes aériennes, comptabilisant à ...
Ce programme permet de suivre l'évolution de la composition, la quantité et de la répartition spatiale, des macro-déchets présents sur les fonds marins. Ce sous-programme repose aujourd'hui sur le dispositif des campagnes halieutiques DCF optimisées - déchets de fond, notamment les campagnes bent...
Ce programme permet de suivre l'évolution de la composition, de la quantité et de la répartition spatiale des micro-déchets (300 µm – 5mm) présents en sub-surface. Ce sous-programme repose sur le dispositif de surveillance « Campagnes halieutiques DCF optimisées – Micro-déchets » qui consiste en ...
Ce programme a pour objectif de suivre la nature et la quantité de déchets ingérés par les oiseaux. La quantité et la nature des déchets ingérés sont suivies selon le protocole préconisé dans le cadre d'OSPAR pour les oiseaux. Ce suivi consiste en l'analyse des déchets contenus dans l'estomac des...
Ce programme permet de suivre la nature et la quantité de déchets ingérés par les tortues marines et dans une moindre mesure par les mammifères marins retrouvés échoués sur le littoral. Il repose principalement sur le dispositif de surveillance « Réseaux de suivi des échouages des tortues marines...
Ce programme permet de suivre l'emmêlement et l'enchevêtrement de la faune marine (oiseaux marins, mammifères marins, tortues marines, faune épibenthique) par les déchets marins. Le suivi de l'emmêlement et enchevêtrement des oiseaux marins repose sur le dispositif de surveillance « Suivi des mac...
En France, la DCSMM est mise en œuvre conjointement avec la directive 2014/89/UE (établissant un cadre pour la planification de l'espace maritime) à travers les documents stratégiques de façade. Dans cette démarche, le document stratégique de façade contribue à améliorer la prise en compte récipr...
The amount of litter on the seabed of the North East Atlantic is monitored as part of existing trawling programmes for the assessment of fish stocks, the International Bottom Trawl Survey. These programmes are coordinated by the International Council for the Exploration of the Seas (ICES). North East Atlantic countries survey different sections of the marine areas. For example, France and Ireland currently survey the Celtic Sea area, Ireland covers the shelf West of Ireland, Ireland and Scotland survey the north coast of Ireland and Northern Ireland covers the Irish Sea.
Beach litter monitoring is undertaken to quantify and characterise litter pollution (items ≥ 2.5 cm) both spatially, around Ireland’s coastline and temporally, over many years. It provides a basis for identifying the main sources of marine litter, and the information required to determine where to target measures to reduce litter entering our seas. As it is repeated over long time-periods, it allows Ireland to identify trends in the types of litter washed up or deposited on the Irish coastline and will provide data on the effectiveness of current, and future, measures to manage and reduce litter. These include those that will be targeted by the Single Use Plastics Directive (SUPD, 2019/904/EEC).
To assess whether GES is achieved for criterion D10C1, information is needed on trends in the quantity and composition of litter on Dutch beaches, on the seabed and floating on the sea surface. The quantity of plastic found in the stomachs of fulmars (Fulmarus glacialis) is used as an indicator for litter on the surface layer. This indicator is also used for D10C3, which relates to the amount of litter ingested by marine animals. Because litter crosses national borders, the monitoring and assessment is regionally coordinated in OSPAR. To gain insight into the sources of pollution and the effectiveness of measures, a distinction is made between different categories of litter. The assessment is carried out at both DCS level and North Sea level. To monitor litter on beaches, surveys are conducted four times a year on four reference beaches in the municipalities of Terschelling, Bergen, Noordwijk and Veere for Rijkswaterstaat. At each location the litter is classified according to the 115 litter types in the OSPAR CEMP Guidelines (OSPAR, 2017). For each type of litter, the number of items per 100 metres is counted along the entire width of the beach. Only items of litter that are visible on the surface are counted. The survey for monitoring plastics in the stomachs of birds has been part of Rijkswaterstaat’s MWTL programme since 2004, but has been operational since 1996. The data are provided every year by volunteers of the Northern fulmar working group, who collect dead Northern fulmars that have washed up along the Dutch coast during the year. Professionals then analyse the contents of the birds’ stomachs to determine the total mass of plastic particles in grams and the total number of particles in the stomach. The plastics found are divided into consumer plastics and industrial plastics (pellets). The method is documented in the OSPAR CEMP Guidelines (OSPAR, 2019). In the coming years, Rijkswaterstaat will carry out pilot projects to develop monitoring methods for macro-litter and micro-plastics in rivers. Although they will not be part of the MSFD monitoring programme, these surveys will provide information about sources and the effectiveness of measures.
To assess whether GES is achieved for criterion D10C1, information is needed on trends in the quantity and composition of litter on Dutch beaches, on the seabed and floating on the sea surface. The quantity of plastic found in the stomachs of fulmars (Fulmarus glacialis) is used as an indicator for litter on the surface layer. This indicator is also used for D10C3, which relates to the amount of litter ingested by marine animals. Because litter crosses national borders, the monitoring and assessment is regionally coordinated in OSPAR. To gain insight into the sources of pollution and the effectiveness of measures, a distinction is made between different categories of litter. The assessment is carried out at both DCS level and North Sea level. The survey for monitoring plastics in the stomachs of birds has been part of Rijkswaterstaat’s MWTL programme since 2004, but has been operational since 1996. The data are provided every year by volunteers of the Northern fulmar working group, who collect dead Northern fulmars that have washed up along the Dutch coast during the year. Professionals then analyse the contents of the birds’ stomachs to determine the total mass of plastic particles in grams and the total number of particles in the stomach. The plastics found are divided into consumer plastics and industrial plastics (pellets). The method is documented in the OSPAR CEMP Guidelines (OSPAR, 2019). In the coming years, Rijkswaterstaat will carry out pilot projects to develop monitoring methods for macro-litter and micro-plastics in rivers. Although they will not be part of the MSFD monitoring programme, these surveys will provide information about sources and the effectiveness of measures.
To assess whether GES is achieved for criterion D10C1, information is needed on trends in the quantity and composition of litter on Dutch beaches, on the seabed and floating on the sea surface. The quantity of plastic found in the stomachs of fulmars (Fulmarus glacialis) is used as an indicator for litter on the surface layer. This indicator is also used for D10C3, which relates to the amount of litter ingested by marine animals. Because litter crosses national borders, the monitoring and assessment is regionally coordinated in OSPAR. To gain insight into the sources of pollution and the effectiveness of measures, a distinction is made between different categories of litter. The assessment is carried out at both DCS level and North Sea level. The survey for monitoring plastics in the stomachs of birds has been part of Rijkswaterstaat’s MWTL programme since 2004, but has been operational since 1996. The data are provided every year by volunteers of the Northern fulmar working group, who collect dead Northern fulmars that have washed up along the Dutch coast during the year. Professionals then analyse the contents of the birds’ stomachs to determine the total mass of plastic particles in grams and the total number of particles in the stomach. The plastics found are divided into consumer plastics and industrial plastics (pellets). The method is documented in the OSPAR CEMP Guidelines (OSPAR, 2019). In the coming years, Rijkswaterstaat will carry out pilot projects to develop monitoring methods for macro-litter and micro-plastics in rivers. Although they will not be part of the MSFD monitoring programme, these surveys will provide information about sources and the effectiveness of measures.
To assess whether GES is achieved for criterion D10C1, information is needed on trends in the quantity and composition of litter on Dutch beaches, on the seabed and floating on the sea surface. The quantity of plastic found in the stomachs of fulmars (Fulmarus glacialis) is used as an indicator for litter on the surface layer. This indicator is also used for D10C3, which relates to the amount of litter ingested by marine animals. Because litter crosses national borders, the monitoring and assessment is regionally coordinated in OSPAR. To gain insight into the sources of pollution and the effectiveness of measures, a distinction is made between different categories of litter. The assessment is carried out at both DCS level and North Sea level. Since 2013, litter on the seabed has been collected as ‘bycatch’ during the International Bottom Trawl Survey (IBTS). The IBTS monitoring is carried out every year for the Ministry of Agriculture, Nature and Food Quality for the purposes of the Common Fisheries Policy (CFP). For the IBTS, ICES quadrants (areas of roughly 56 x 56 km) are sampled with a standard bottom trawl, the Grand Ouverture Verticale (GOV). Every area is fished in accordance with the standard ICES protocol. Litter that surfaces in the process is classified according to a list of forty types of litter. The number of items of each type of litter is registered during each 30-minute trawl, and the swept area is calculated, leading to litter counts per km2. The method to be used is laid down in the OSPAR CEMP Guidelines (OSPAR, 2017). In the coming years, Rijkswaterstaat will carry out pilot projects to develop monitoring methods for macro-litter and micro-plastics in rivers. Although they will not be part of the MSFD monitoring programme, these surveys will provide information about sources and the effectiveness of measures.
No GES has yet been established for micro-litter (D10C2), but OSPAR is expected to formulate an indicator in 2020. A new monitoring survey for micro-litter in sediment is expected to be launched at the beginning of 2021. The survey to be developed for monitoring at sea will have to be compatible with the technical specifications that are ultimately adopted in OSPAR’s CEMP Guidelines. Although not yet finalised, the following specifications are being considered: • Spatial coverage: the DCS will be sampled at multiple locations, with the greatest density in the coastal zone since that is where the largest concentrations are. • Monitoring frequency: a limited number of locations in the coastal zone will be sampled annually to allow for an analysis of the trend after five years of measurements. Monitoring every three years is sufficient for the other locations. • Method: methods being considered to allow quantitative analysis are sampling with box core (subtidal) or trowel (intertidal). Parameters: the total number of microplastic particles in each sample and the total mass (per kg dry weight) will be determined in the sand fraction. Only the top layer (to a depth of 5 cm) will be sampled because that is where the highest concentration of microplastics occur and the greatest changes are observed. The upper size limit for microplastic particles is 5 mm.
O programa de monitorização proposto visa responder ao critério D10C1, no que se refere ao macrolixo presente na superfície da coluna de água, e será implementado nas subdivisões dos Açores e da Madeira, de acordo com as diretrizes do Guia JRC Guidance on Monitoring of Marine Litter in European S...
Este programa tem o objetivo principal de recolher dados sobre a pescaria de palangre de superfície através de observadores a bordo de embarcações portuguesas. Este programa contribui para a monitorização dos descritores D1 e D10.
Este programa tem o objetivo de colmatar lacunas de recolha de dados para espécies e ecossistemas costeiros e ao mesmo tempo de se articular com outros PMOs (PT-MO-D3; PT-MO-IntroNIS-AMP; PT-MO-D6-HB-INT-ROC; PT-MO-D6-INT-SED; e PT-AZO-MO-POPA), de forma a que a subdivisão Açores possa dar respos...
No âmbito do DL102/2020, de 9 de dezembro, que transpõe a Diretiva (UE) 2019/883, relativa aos meios portuários de receção de resíduos provenientes dos navios, tendo em vista uma maior proteção do meio marinho, as autoridades portuárias e gestoras de portos são obrigadas a implementar medidas de ...
Este programa pretende monitorizar a ingestão e o impacto do macrolixo e microlixo marinho na biota (cetáceos, répteis, aves e peixes), respondendo assim aos critérios D10C3 e D10C4. O programa de monitorização será implementado nas subdivisões do Continente, Madeira e Açores. De acordo com o rel...
O programa de monitorização de macrolixo na orla costeira/praias será realizado de acordo com as diretrizes do Protocolo OSPAR para a monitorização de Lixo Marinho nas praias da Área Marítima OSPAR (OSPAR, 2010), e reportadas no Banco de Dados de Lixo de Praia da OSPAR (OSPAR,2021). Em 2020, o G...
O programa de monitorização proposto visa responder ao critério D10C1, no que se refere ao macrolixo presente nos fundos marinhos, e será implementado nas subdivisões do Continente, Açores e Madeira, de acordo com as diretrizes definidas pelo Guia JRC Guidance on Monitoring of Marine Litter in Eu...
O programa de monitorização proposto visa responder ao critério D10C2, no que se refere ao microlixo presente nas praias, e será implementado nas subdivisões Continente, Açores e Madeira, de acordo com as diretrizes definidas pelo Guia JRC Guidance on Monitoring of Marine Litter in European Seas....
O programa de monitorização proposto visa responder ao critério D10C2, no que se refere ao microlixo presente na camada superficial da coluna de água e nos fundos marinhos, e será implementado de acordo com as diretrizes definidas pelo Guia JRC Guidance on Monitoring of Marine Litter in European ...
The purpose of the monitoring is to measure the amount of litter that has ended up on beaches either by input from the sea, or from land. There are geographical differences in the type of litter found, but ropes, strings and fishing lines as well as cigarette butts, plastic bags, disposable plastic items and wrappers for sweets and ice cream, etc. are common litter items on beaches. Plastic pieces of different sizes that cannot be traced to a specific object are also common. The majority of the litter consists of plastic material (approximately 70-95%). The effects of litter have been demonstrated by, for example, entanglement of marine animals and by ingestion of litter by birds, fish and invertebrates. However, the extent and impact of the effects are still a subject of research. Monitoring can also help to measure the effects of human impact and measures, by analyzing in detail the presence of different categories of litter. Monitoring in the North Sea started in 2001 while in the Baltic Sea it started in 2014. Monitoring should be carried out four times a year on each beach, but due to possible ice and snow, measurements are not carried out during the winter in Sweden. The beaches are monitored during spring (April), summer (mid-June to mid-July) and autumn (mid-September to mid-October).
The development of internationally standardized methods for sampling and analysis of microlitter is ongoing, which is why no ongoing monitoring have yet started in Sweden. The Swedish EPA and SwAM participate with experts in international expert groups and research projects to develop internationally common standards for sampling and analysis of microlitter. This work also includes developing indicators with threshold values in order to be able to assess status. Several studies have been conducted to map the amount of microlitter in water, sediment and on beaches. During the spring of 2020, monitoring of hazardous substances in sediments was carried out (see programme Hazardous substances in sediments) and for the first time additional samples were collected with the purpose of analyzing microlitter. The results of the effort will be evaluated and, if successful, microlitter will be added to the ongoing monitoring, which is repeated every six years. The starting year 2020 is therefore preliminary, as we do not yet know whether the monitoring will be repeated in 2026.
Litter that ends up in the sea can float around, get washed up on beaches or end up on the seabed. In order to get as comprehensive information as possible of the presence of marine litter, macro litter on the seabed is monitored within the framework of international trawl surveys to estimate fish stocks, where demersal trawls are used. Examples of litter objects found on the bottom are fishing lines, synthetic ropes, fishing nets, plastic bags and cans. Plastic objects are most common. The Skagerrak-Kattegat includes litter monitoring in the national coastal trawl trawling and in the International Bottom Trawl Survey (IBTS). In the Baltic Sea, it is part of the international program BITS (Baltic International Trawl Survey). The effects of litter have been demonstrated through, for example, the entaglement of marine animals and the ingestion of litter by birds, fish and invertebrates. However, the extent and impact of the effects are still the subject of research. Monitoring can also help to measure the effects of human impact and measures, by analyzing in detail the presence of different categories of litter.
Monitoring purpose
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures at source
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Environmental state and impacts
  • Human activities causing the pressures
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Environmental state and impacts
  • Human activities causing the pressures
  • Pressures in the marine environment
  • Environmental state and impacts
  • Pressures in the marine environment
  • Pressures in the marine environment
  • Effectiveness of measures
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Pressures in the marine environment
  • Environmental state and impacts
  • Environmental state and impacts
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
  • Effectiveness of measures
  • Pressures in the marine environment
Other policies and conventions
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • HELCOM Monitoring programmes
  • OSPAR Coordinated Environmental Monitoring Programme
  • HELCOM Monitoring programmes
  • OSPAR Coordinated Environmental Monitoring Programme
  • HELCOM Monitoring programmes
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • UNEP-MAP Integrated Monitoring and Assessment Programme
  • UNEP-MAP Integrated Monitoring and Assessment Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • UNEP-MAP Integrated Monitoring and Assessment Programme
  • UNEP-MAP Integrated Monitoring and Assessment Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • UNEP-MAP Integrated Monitoring and Assessment Programme
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • NEAFC Monitoring of Fisheries
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • International Commission for the Conservation of Atlantic Tunas
  • OSPAR Coordinated Environmental Monitoring Programme
  • Data Collection Framework Multi-Annual Plan (Common Fisheries Policy)
  • Habitats Directive
  • Monitoring programme targeting at national legislation
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • OSPAR Coordinated Environmental Monitoring Programme
  • Bathing Water Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Water Framework Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Water Framework Directive
  • HELCOM Monitoring programmes
  • Maritime Spatial Planning Directive
  • Monitoring programme targeting at national legislation
  • OSPAR Coordinated Environmental Monitoring Programme
  • Water Framework Directive
Regional cooperation - coordinating body
  • OSPAR
  • Other
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • Other
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
  • BARCON
  • OSPAR
  • BARCON
  • BARCON
  • OSPAR
  • BARCON
  • OSPAR
  • BARCON
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • OSPAR
  • HELCOM
  • OSPAR
  • HELCOM
  • OSPAR
Regional cooperation - countries involved
  • BE
  • DE
  • DK
  • FR
  • NL
  • PL
  • SE
  • UK
  • NL
  • NL
Regional cooperation - implementation level
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Agreed data collection methods
Common monitoring strategy
Joint data collection
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Coordinated data collection
Coordinated data collection
Agreed data collection methods
Coordinated data collection
Common monitoring strategy
Coordinated data collection
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Common monitoring strategy
Agreed data collection methods
Agreed data collection methods
Coordinated data collection
Coordinated data collection
Coordinated data collection
Coordinated data collection
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Agreed data collection methods
Common monitoring strategy
Common monitoring strategy
Coordinated data collection
Monitoring details
Existing monitoring between 2002 - 2006 during the summer; restarted 2012 (spring). Monitoring at a new location from 2020 onwards.
Yearly monitoring since 2011, 5 locations per year at the BPNS.
Yearly sample size of useful specimens of northern fulmars may highly differ (eg. varied between 1 and 97 between 2001 and 2006). Yearly plastic loads will be reported at the level of OSPAR regions. Van Franeker, J.A.; Blaize, C.; Danielsen, J.; Fairclough, K.; Gollan, J.; Guse, N.; Hansen, P.-L.; Heubeck, M.; Jensen, J.-K.; Le Guillou, G.; Olsen, B.; Olsen, K.-O.; Pedersen, J.; Stienen, E.W.M.; Turner, D.M. (2011). Monitoring plastic ingestion by the northern fulmar Fulmarus glacialis in the North Sea. Environmental Pollution 159: 2609-2615. dx.doi.org/10.1016/j.envpol.2011.06.008
|| MP_51 ||
|| MP_66 || Vierteljährlich stattfindenden Kontrollen beinhalteten die Detailerfassung alle Müllteile auf einem 100 m Strandabschnitt. Insgesamt 112 Müllkategorien aus zehn Hauptkategorien (Gummi, Stoff, Papier, Pappe, Holz [bearbeitet], Metall, Glas, Porzellan/Keramik, Sanitärartikel, Medizinart...
|| MP_67 ||
|| MP_68 || Menge von Makromüll am Meeresboden wird nach IBTS Klassifizierung erhoben.
|| MP_71 ||
|| MP_73 || Investigatives Monitoring im Rahmen von FuE-Vorhaben
|| MP_262 || - Zusammenstellung komplexe Schadstoffunfälle- Erfassung lokale Belastungsschwerpunkte- Erfassung Grundbelastungen durch Zählrahmen an zwei Stränden- Auswertung vorliegender Daten aus dem OSPAR-Spülsaummonitoring in DE (Nord- und Ostsee) - Erfassung in der Oberflächenschicht der Wassersäule
|| MP_70 || Investigatives Monitoring im Rahmen von F&E-Vorhaben. Dies umfasst die Entwicklung eines automatischen Probenahmegerätes für suspendiertes Mikroplastik in Küsten- und Übergangsgewässern.
Det bliver i den kommende programperiode undersøgt om det er fordelagtigt at bruge andre indikator-organismer end sild og torsk eller evt. inddrage tilfældige forekomster (f.eks. strandinger af døde dyr) til overvågning af affald i biota. Det er hensigten at affald i biota overvåges min. to gange i programperioden.
Fiskere er under den EUs Fælles Fiskeripolitik forpligtet til at indrapportere tabte fiskeredskaber til Fiskeristyrelsen https://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:32009R1224 https://fiskeristyrelsen.dk/erhvervsfiskeri/indberetning-og-foering-af-logbog/tabte-redskaber/
Prøveindsamlingen koordineres med analyseprogrammet for miljøfarlige stoffer i sedimenter. Forekomsten og identifikation af typen af mikroaffald i sedimentet analyseres ved at adskille mikroaffaldet fra det organiske materiale, og mikroaffaldet inddeles herefter i to størrelsesfraktioner. Herefter undersøges den kemiske sammensætning.
En las campañas anuales llevadas a cabo por el IEO, como PELACUS o MEDIAS en paralelo al resto de actividades que se llevan a cabo, se realizan monitoreos mediante censos visuales de la presencia y composición de las basuras flotantes en las estaciones de muestreo definidas con los/as jefes/as de...
Observations on litter deposited on the seabed are obtained during campaigns in charge of assessing benthic and demersal resources. These campaigns generally take place during the autumn winter transition between September and October. Fishing hauls are carried out during the day using “Baka”...
Para el muestreo de micropartículas en superficie y columna de agua se aplicauna adaptación de la metodología recogida en Viršek et al., (2016). En las estaciones de muestreo determinadas con los/as jefes/as de campaña se realizan pescas de arrastre superficiales con manta trawl (330 μm) de una ...
The sampling strategy was designed taking into account the highly heterogeneous distribution of microplastics in sediments (Wang et al., 2018) together with the aims of different working groups to analyse, inter alia: PAH, PCB, OCP, PBDE or trace metals. Sediment was sampled using a stainless ste...
Seabed litter monitoring is undertaken by the Marine Institute in Ireland. The Irish Groundfish Survey (IGFS) is carried out over 42 days in the autumn/winter annually using the R.V. Celtic Explorer (65 m vessel). Each year 170 stations are randomly selected to be surveyed. A high headline Overture Vertical (GOV) trawl with a 20 mm coded liner is used to survey the stations over 30 minutes at 4 knots. Sampling is stratified into 17 strata by depth and ICES sub-region. The net area sampled at each station is estimated from the width of the net by the distance trawled. The seabed litter collected is sorted, counted and normalised to km2. The IGFS collects data from four ICES Subregions – 27.6a, 27.7b, 27.7j and 27.7g. Following quality control, data is uploaded to the ICES DATRAS database.
Beach litter monitoring is undertaken 4 times annually, once per quarter, at four beaches around Ireland. The surveys are undertaken at Long Strand Beach, Co. Cork (51°33'8.253''N), Silver Strand Beach, Co. Mayo (53°38'45.073''N), Carnsore, Co. Wexford (52°11'31.932''N) and Clougherhead-South, Co. Louth (53°47'19.494''N). The surveys are undertaken using the standardized methodology created by OSPAR. This allows for regional interpretation of the results and comparisons between difference geographical regions in Europe. The same 100 m stretch of beach is monitored during every survey. The litter collected is catalogued according to regionally agreed lists (Table 10.3). Following quality controls, data is held in a national database and uploaded to the OSPAR Beach litter database.
To monitor litter on beaches, surveys are conducted four times a year on four reference beaches in the municipalities of Terschelling, Bergen, Noordwijk and Veere for Rijkswaterstaat. At each location the litter is classified according to the 115 litter types in the OSPAR CEMP Guidelines (OSPAR, 2017). For each type of litter, the number of items per 100 metres is counted along the entire width of the beach. Only items of litter that are visible on the surface are counted.
Na subdivisão da Madeira, a monitorização será coordenada pela Agência Regional para o Desenvolvimento da Investigação, Tecnologia e Inovação (ARDITI), através do Centro de Ciências do Mar e do Ambiente (MARE). Serão monitorizadas 4 zonas de superfície de mar adjacentes às seguintes praias da ilh...
O COSTA é um programa de observação da pescaria portuguesa de palangre de superfície dirigido ao espadarte e tintureira, coordenado pelo Programa de Monitorização PT-AZO-MO-POPA, tendo a colaboração de dois observadores a tempo inteiro. Desta forma permite recolher dados sobre as capturas das esp...
As ações de monitorização específicas previstas neste programa baseiam-se em diferentes módulos com diversas metodologias de monitorização (independentes da pesca) para diferentes ecossistemas, habitats e recursos costeiros: i) Apanha (monitorização por transetos para contagem e recolha de lapas)...
Pretende-se desenvolver protocolos com recomendações técnicas para recolha de resíduos em Portos comerciais, Portos de pesca e Marinas, ajustadas à realidade dos portos portugueses e também disponibilizar uma ferramenta georeferenciada de reporte que permita conhecer as características, quantidad...
Para a monitorização de lixo e microlixo em peixes, na subdivisão da Madeira, foi selecionada a espécie Scomber colias. No âmbito do Plano Nacional de Recolha de Dados (PNRD) e do Plano Nacional de Amostragem Biológica (PNAB), serão amostrados anualmente 50 exemplares para pesquisa de lixo e micr...
A recolha de dados consiste numa amostragem sazonal (inverno, primavera, verão e outono) em 22 praias (12 no Continente, 6 nos Açores, 4 na Madeira), em todo o território nacional, em secções de praia fixas de 100 metros (podendo ir até um mínimo de 70 metros). Todos os itens de lixo encontrados ...
Na subdivisão do Continente, a monitorização tem por base informação de macrolixo presente nos fundos marinhos que é recolhido nos lances de pesca com arte de arrasto pelo fundo, efetuados durante as campanhas de investigação do IPMA no âmbito do PNAB. Embora seja uma monitorização oportunista, p...
A recolha de dados será realizada em 29 praias (10 nos Açores, 7 na Madeira, 12 no Continente), amostrando uma camada de areia de 50x50x5cm de areia na zona de linha da maré alta, ao longo de 100m, perfazendo um total de 5 réplicas, com uma distância de 25m entre elas. Todos os itens de microlixo...
Na subdivisão da Madeira, a monitorização de microlixo na coluna de água será coordenada pela Agência Regional para o Desenvolvimento da Investigação, Tecnologia e Inovação (ARDITI), através do Centro de Ciências do Mar e do Ambiente (MARE). Será realizada uma vez por ano, nas zonas adjacentes às...
Coastal fish
  • Bodianus scrofa
  • Diplodus sargus cadenati
  • Mycteroperca fusca
  • Seriola rivoliana
  • D1C2
  • Abundance (number of individuals)
Demersal shelf fish
  • Squalus acanthias
  • D1C2
  • D1C4
  • D1C5
  • Abundance (number of individuals)
  • Distribution (range)
  • Distribution (spatial)
  • Extent
Deep-sea fish
  • Deania calcea
  • Etmopterus princeps
  • Etmopterus pusillus
  • Etmopterus spinax
  • Galeus melastomus
  • Helicolenus dactylopterus
  • Phycis blennoides
  • D1C2
  • D1C4
  • D1C5
  • Abundance (number of individuals)
  • Distribution (range)
  • Distribution (spatial)
  • Extent
Commercially exploited fish and shellfish
  • Aequipecten opercularis
  • Cancer pagurus
  • Capros aper
  • Carcinus maenas
  • Centrolabrus exoletus
  • Cerastoderma edule
  • Chelidonichthys cuculus
  • Chelidonichthys lucerna
  • Clupea harengus
  • Conger conger
  • Dasyatis pastinaca
  • Dicentrarchus labrax
  • Dipturus oxyrinchus
  • Ensis Magnus
  • Ensis Siliqua
  • Eutrigla gurnardus
  • Gadus morhua
  • Galeorhinus galeus
  • Glyptocephalus cynoglossus
  • Helicolenus dactylopterus
  • Homarus gammarus
  • Illex coindetii
  • Lepidorhombus whiffiagonis
  • Leucoraja circularis
  • Leucoraja fullonica
  • Leucoraja naevus
  • Limanda limanda
  • Lophius budegassa
  • Lophius piscatorius
  • Maja squinado
  • Melanogrammus aeglefinus
  • Merluccius merluccius
  • Micromesistius poutassou
  • Molva molva
  • Mora moro
  • Mustelus asterias
  • Mytilus edulis
  • Necora puber
  • Nephrops norvegicus
  • Ostrea edulis
  • Pagellus bogaraveo
  • Palaemon Serratus
  • Palinurus elephas
  • Pecten maximus
  • Phycis blennoides
  • Platichthys flesus
  • Pleuronectes platessa
  • Pollachius pollachius
  • Pollachius virens
  • Prionace glauca
  • Raja brachyura
  • Raja clavata
  • Raja microocellata
  • Raja montagui
  • Raja undulata
  • Sardina pilchardus
  • Scomber scombrus
  • Scophthalmus maximus
  • Scophthalmus rhombus
  • Scyliorhinus canicula
  • Solea solea
  • Spisula solida
  • Sprattus sprattus
  • Squalus acanthias
  • Thunnus alalunga
  • Thunnus thynnus
  • Trachurus trachurus
  • Trisopterus luscus
  • Zeus faber
  • D3C1
  • D3C2
  • Mortality (weight/volume; number of individuals)
  • Mortality rate
  • Abundance (number of individuals)
  • Other
  • Biomass of Spawning Stock (SSB)
  • Biomass
  • D
  • Distribution - Range
  • Patella aspera
  • Sparisoma cretense
  • D3C1
  • D3C2
  • D3C3
  • Other
  • Catch/Biomass ratios
  • L95 percentile of length distribution
  • Trend analyses (abundance indices)
Benthic broad habitats
  • Infralittoral coarse sediment
  • Infralittoral mixed sediment
  • Infralittoral mud
  • Infralittoral rock and biogenic reef
  • Infralittoral sand
  • Littoral rock and biogenic reef
  • Littoral sediment
  • D6C3
  • D6C4
  • D6C5
  • Extent
Input or spread of non-indigenous species
  • Not Applicable
  • D2C1
  • D2C2
  • Distribution (spatial)
  • Presence
  • Abundance (number of individuals)
Extraction of, or mortality/injury to, wild species (by commercial and recreational fishing and other activities)
  • Not Applicable
  • D1C1
  • D1C4
  • D1C5
  • D6C2
  • Mortality (weight/volume; number of individuals)
  • Mortality rate
  • Distribution (range)
  • Distribution (spatial)
  • Extent
Input of litter (solid waste matter, including micro-sized litter)
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Amount on seabed
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Amount on seabed
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Amount on seabed
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Amount on seabed
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Amount on seabed
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Amount on seabed
  • Macrolitter (all)
  • NotRelevan
  • Amount on coastline
  • Not Applicable
  • D10C1
  • Amount on water surface
  • Not Applicable
  • D10C1
  • Amount on coastline
  • Not Applicable
  • D10C1
  • Other
  • Amount on seabed
  • Not Applicable
  • D10C2
  • Amount on coastline
  • Not Applicable
  • D10C2
  • Amount on seabed
  • Amount on water surface
Newly introduced non-indigenous species
  • Not Applicable
  • D2C1
  • Distribution (spatial)
  • Presence
Eutrophication
Contaminants - non UPBT substances
Contaminants - UPBT substances
Acute pollution events
Litter in the environment
  • Litter in the environment
  • D10C1
  • Amount on coastline
  • Macrolitter (all)
  • D10C1
  • Amount on seabed
  • Macrolitter (all)
  • D10C3
  • Amount in biota (ingested)
  • Artificial polymer materials
  • Ceramics/pottery
  • Cloth/textile
  • Glass/ceramics
  • Medical waste
  • Metal
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on coastline
  • Artificial polymer materials
  • Glass/ceramics
  • Metal
  • Other materials
  • Rubber
  • Undefined
  • D10C1
  • Amount on seabed
  • Miscellaneous
  • natural products
  • Artificial polymer materials
  • Cloth/textile
  • Glass/ceramics
  • Metal
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • D10C1
  • Amount on water surface
  • Chemicals
  • D10C1
  • Amount on coastline
  • Amount on water surface
  • Artificial polymer materials
  • Ceramics/pottery
  • Cloth/textile
  • Food waste
  • Glass/ceramics
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on coastline
  • Artificial polymer materials
  • Cloth/textile
  • Glass/ceramics
  • Metal
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on seabed
  • Other materials
  • D10C1
  • Other
  • Tabte fiske redskaber
  • Artificial polymer materials
  • Ceramics/pottery
  • Cloth/textile
  • Glass/ceramics
  • Medical waste
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on coastline
  • Artificial polymer materials
  • Cloth/textile
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • D10C1
  • Amount on water surface
  • Other
  • • Patrón de distribución (DIST-P) • Distribución e
  • Artificial polymer materials
  • Ceramics/pottery
  • Cloth/textile
  • Glass/ceramics
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on seabed
  • Other
  • Patrón de distribución, Distribución espacial, Ran
  • Artificial polymer materials
  • Ceramics/pottery
  • Cloth/textile
  • Glass/ceramics
  • Medical waste
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • AMO-WC
  • Amount on coastline
  • Amount on water surface
  • Ceramics/pottery
  • Cloth/textile
  • Glass
  • Litter in the environment
  • Medical waste
  • Metal
  • Paper/cardboard
  • Plastic/polystyrene
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on coastline
  • Other
  • TEND-S1: Tendance dans les sédiments (littoral)
  • Artificial polymer materials
  • Chemicals
  • Litter in the environment
  • Metal
  • Processed/worked wood
  • Undefined
  • D10C1
  • Amount on water surface
  • Other
  • TEND-W1: Tendance dans l'eau
  • Artificial polymer materials
  • Cloth/textile
  • Glass/ceramics
  • Litter in the environment
  • Metal
  • Rubber
  • Undefined
  • D10C1
  • Amount on seabed
  • Other
  • TEND-SB1: Tendance dans les sédiments (fonds marin
  • Ceramics/pottery
  • Cloth/textile
  • Glass
  • Litter in the environment
  • Medical waste
  • Metal
  • Paper/cardboard
  • Plastic/polystyrene
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on coastline
  • Other
  • TEND-S1: Tendance dans les sédiments (littoral)
  • Artificial polymer materials
  • Chemicals
  • Litter in the environment
  • Metal
  • Processed/worked wood
  • Undefined
  • D10C1
  • Amount on water surface
  • Other
  • TEND-W1: Tendance dans l'eau
  • Artificial polymer materials
  • Cloth/textile
  • Glass/ceramics
  • Litter in the environment
  • Metal
  • Rubber
  • Undefined
  • D10C1
  • Amount on seabed
  • Other
  • TEND-SB1: Tendance dans les sédiments (fonds marin
  • Ceramics/pottery
  • Cloth/textile
  • Glass
  • Litter in the environment
  • Medical waste
  • Metal
  • Paper/cardboard
  • Plastic/polystyrene
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on coastline
  • Other
  • TEND-S1: Tendance dans les sédiments (littoral)
  • Artificial polymer materials
  • Chemicals
  • Litter in the environment
  • Metal
  • Processed/worked wood
  • Undefined
  • D10C1
  • Amount on water surface
  • Other
  • TEND-W1: Tendance dans l'eau
  • Artificial polymer materials
  • Cloth/textile
  • Glass/ceramics
  • Litter in the environment
  • Metal
  • Rubber
  • Undefined
  • D10C1
  • Amount on seabed
  • Other
  • TEND-SB1: Tendance dans les sédiments (fonds marin
  • Artificial polymer materials
  • Cloth/textile
  • Glass/ceramics
  • Litter in the environment
  • Macrolitter (all)
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • D10C1
  • Other
  • Amount on seabed
  • amount on seabed
  • Artificial polymer materials
  • Ceramics/pottery
  • Chemicals
  • Cloth/textile
  • Food waste
  • Glass/ceramics
  • Litter in the environment
  • Macrolitter (all)
  • Medical waste
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • Undefined
  • D10C1
  • Amount on coastline
  • Artificial polymer materials
  • Ceramics/pottery
  • Cloth/textile
  • Glass/ceramics
  • Medical waste
  • Metal
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • D10C1
  • Amount on coastline
  • Artificial polymer materials
  • D10C1
  • Mass
  • Artificial polymer materials
  • Glass/ceramics
  • Metal
  • Other materials
  • Rubber
  • D10C1
  • Amount on seabed
  • Artificial polymer materials
  • Glass/ceramics
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • D10C1
  • Amount on water surface
  • Artificial polymer materials
  • Ceramics/pottery
  • Cloth/textile
  • Glass/ceramics
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • D10C1
  • Other
  • Abundância no fundo
  • Abundência no fundo
  • Litter in the environment
  • D10C1
  • Amount on coastline
  • Amount on water surface
  • Other
  • Fundos marinhos
  • Artificial polymer materials
  • Cloth/textile
  • Glass/ceramics
  • Metal
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Undefined
  • D10C1
  • Amount on coastline
  • Artificial polymer materials
  • Ceramics/pottery
  • Glass/ceramics
  • Metal
  • Other materials
  • Processed/worked wood
  • Rubber
  • D10C1
  • Other
  • Amount on seabed
  • Artificial polymer materials
  • Ceramics/pottery
  • Chemicals
  • Cloth/textile
  • Food waste
  • Glass/ceramics
  • Medical waste
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • Undefined
  • D10C1
  • Amount on coastline
  • Artificial polymer materials
  • Ceramics/pottery
  • Chemicals
  • Cloth/textile
  • Food waste
  • Glass/ceramics
  • Medical waste
  • Metal
  • Other materials
  • Paper/cardboard
  • Processed/worked wood
  • Rubber
  • Sanitary waste
  • Undefined
  • D10C1
  • Amount on seabed
Micro-litter in the environment
  • Artificial polymer materials
  • D10C2
  • Concentration in sediment (total)
  • Concentration in water
  • Artificial polymer materials
  • D10C2
  • Other
  • Antal partikler pr kg sediment
  • Artificial polymer materials
  • D10C2
  • Amount on water surface
  • Artificial polymer materials
  • D10C2
  • Amount on water surface
  • Other
  • Patrón de distribución (DIST-P) • Distribución esp
  • Artificial polymer materials
  • D10C2
  • Amount on seabed
  • Other
  • • Concentración en sedimento (CONT-S) • Patrón de
  • Artificial polymer materials
  • D10C2
  • Amount on coastline
  • Other
  • • Concentración en sedimento (total) (CONC-S)
  • Artificial polymer materials
  • D10C2
  • Amount on water surface
  • Other
  • TEND-W1: Tendance dans l'eau
  • Artificial polymer materials
  • D10C2
  • Amount on water surface
  • Artificial polymer materials
  • D10C2
  • Amount on water surface
  • Artificial polymer materials
  • D10C2
  • Concentration in sediment (total)
  • Mass
  • Artificial polymer materials
  • Other materials
  • D10C2
  • Amount on coastline
  • Artificial polymer materials
  • D10C2
  • Amount on seabed
  • Amount on water surface
  • Artificial polymer materials
  • Other materials
  • D10C2
  • Amount on coastline
  • Amount on seabed
  • Amount on water surface
Litter and micro-litter in species
  • Artificial polymer materials
  • D10C3
  • Amount in biota (ingested)
  • Artificial polymer materials
  • Other materials
  • D10C3
  • Amount in biota (ingested)
  • Artificial polymer materials
  • Other materials
  • D10C3
  • Mass
  • Other
  • Number of items
  • Artificial polymer materials
  • D10C3
  • Mass
  • Other
  • Antal
  • Artificial polymer materials
  • Other materials
  • D10C3
  • Mass
  • Artificial polymer materials
  • D10C3
  • Amount in biota (ingested)
  • Artificial polymer materials
  • D10C4
  • Amount in biota (ingested)
  • Artificial polymer materials
  • D10C3
  • Amount in biota (ingested)
  • Artificial polymer materials
  • D10C4
  • Amount in biota (ingested)
  • Artificial polymer materials
  • D10C3
  • Amount in biota (ingested)
  • Artificial polymer materials
  • D10C3
  • Amount in biota (ingested)
  • Artificial polymer materials
  • D10C4
  • Amount in biota (ingested)
  • Artificial polymer materials
  • D10C3
  • Mass
  • Artificial polymer materials
  • D10C3
  • Other
  • Quantificação do peso de itens de lixo no sistema
  • Artificial polymer materials
  • Other materials
  • D10C3
  • Mass
Impulsive sound in water
Continuous low frequency sound
Adverse effects on species or habitats
  • Morus bassanus
  • Uria aalge
  • D10C4
  • Mortality (weight/volume; number of individuals)
Species affected by incidental by-catch
  • Not Applicable
  • D1C1
  • Mortality (weight/volume; number of individuals)
  • Mortality rate
  • Not Applicable
  • D1C1
  • Mortality (weight/volume; number of individuals)
  • Mortality rate
Spatial scope
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Terrestrial part of MS
  • EEZ (or similar)
  • Territorial waters
  • Terrestrial part of MS
  • Terrestrial part of MS
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • Terrestrial part of MS
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • Continental shelf (beyond EEZ)
  • Beyond MS Marine Waters
  • EEZ (or similar)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • Territorial waters
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • Terrestrial part of MS
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Terrestrial part of MS
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Terrestrial part of MS
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • EEZ (or similar)
  • Territorial waters
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
  • Coastal waters (WFD)
  • Continental shelf (beyond EEZ)
  • EEZ (or similar)
  • Territorial waters
  • Transitional waters (WFD)
  • Terrestrial part of MS
  • EEZ (or similar)
  • EEZ (or similar)
  • EEZ (or similar)
  • Beyond MS Marine Waters
  • EEZ (or similar)
  • Coastal waters (WFD)
  • Territorial waters
  • EEZ (or similar)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Coastal waters (WFD)
  • Terrestrial part of MS
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • Territorial waters
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • Territorial waters
  • Terrestrial part of MS
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Terrestrial part of MS
  • Territorial waters
  • Beyond MS Marine Waters
  • Coastal waters (WFD)
  • EEZ (or similar)
  • Territorial waters
Marine reporting units
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANS-BE-MS-1
  • ANSDE_EEZ
  • ANSDE_MS
  • ANSDE_MS
  • ANSDE_MS
  • ANSDE_MS
  • ANSDE_MS
  • ANSDE_MS
  • ANSDE_MS
  • ANS-DK-TOTAL
  • DK-TOTAL
  • DK-TOTAL-WO_coast
  • ANS-DK-TOTAL
  • BAL-DK-SEA_001
  • BAL-DK-SEA_003
  • BAL-DK-SEA_006
  • BAL-DK-SEA_007
  • BAL-DK-SEA_05
  • BAL-DK-SEA_06
  • BAL-DK-SEA_07
  • BAL-DK-SEA_09
  • DK-ANS-ICES
  • DK-BAL-EAST-ICES
  • DK-BAL-WEST-ICES
  • DK-TOTAL
  • DK-TOTAL
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-ES-SD-NOR
  • ABI-ES-SD-SUD
  • AMA-ES-SD-CAN
  • MWE-ES-SD-ESAL
  • MWE-ES-SD-LEV
  • ABI-FR-MS-GDG-NORD
  • ABI-FR-MS-GDG-SUD
  • ABI-FR-MS-GDG-NORD
  • ABI-FR-MS-GDG-SUD
  • ABI-FR-MS-GDG-NORD
  • ABI-FR-MS-GDG-SUD
  • ABI-FR-MS-GDG-NORD
  • ABI-FR-MS-GDG-SUD
  • ABI-FR-MS-GDG-NORD
  • ABI-FR-MS-GDG-SUD
  • ABI-FR-MS-GDG-NORD
  • ABI-FR-MS-GDG-SUD
  • ABI-FR-MS-GDG-NORD
  • ABI-FR-MS-GDG-SUD
  • ACS-FR-MS-MC
  • ACS-FR-MS-MC
  • ACS-FR-MS-MC
  • ACS-FR-MS-MC
  • ACS-FR-MS-MC
  • ACS-FR-MS-MC
  • ACS-FR-MS-MC
  • ANS-FR-MS-MMN
  • ANS-FR-MS-MMN
  • ANS-FR-MS-MMN
  • ANS-FR-MS-MMN
  • ANS-FR-MS-MMN
  • ANS-FR-MS-MMN
  • ANS-FR-MS-MMN
  • ANS-FR-MS-MMN
  • ACS-IE-AA-001
  • ACS-IE-AA-001
  • ANS-NL-MS-1
  • ANS-NL-MS-1
  • L1.2
  • ANS-NL-MS-1
  • L1.2
  • L1.2
  • ANS-NL-MS-1
  • AMA-PT-SD-AZO
  • AMA-PT-SD-MAD
  • AMA-PT-SD-AZO
  • AMA-PT-SD-AZO
  • ABI-PT-SD-CONT
  • ABI-PT-AA-CONT_AT
  • ABI-PT-AA-CONT_BT1
  • ABI-PT-AA-CONT_CT
  • AMA-PT-SD-AZO
  • AMA-PT-SD-MAD
  • ABI-PT-AA-CONT_AT
  • ABI-PT-AA-CONT_BT1
  • ABI-PT-AA-CONT_CT
  • AMA-PT-SD-AZO
  • AMA-PT-SD-MAD
  • ABI-PT-AA-CONT_AT
  • ABI-PT-AA-CONT_BT1
  • ABI-PT-AA-CONT_CT
  • AMA-PT-SD-AZO
  • AMA-PT-SD-MAD
  • ABI-PT-AA-CONT_AT
  • ABI-PT-AA-CONT_BT1
  • ABI-PT-AA-CONT_CT
  • AMA-PT-SD-AZO
  • AMA-PT-SD-MAD
  • ABI-PT-AA-CONT_AT
  • ABI-PT-AA-CONT_BT1
  • ABI-PT-AA-CONT_CT
  • AMA-PT-SD-AZO
  • AMA-PT-SD-MAD
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Oresund
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Alands_hav
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_Bottenhavet
  • BAL-SE-AA-B_Bottenviken
  • BAL-SE-AA-B_N_Gotlandshavet
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
  • ANS-SE-AA-B_Kattegatt
  • ANS-SE-AA-B_Skagerrak
  • BAL-SE-AA-B_Arkonahavet_och_S_Oresund
  • BAL-SE-AA-B_Bornholmshavet_och_Hanobukten
  • BAL-SE-AA-B_O_Gotlandshavet
  • BAL-SE-AA-B_V_Gotlandshavet
Temporal scope (start date - end date)
2012-9999
2011-9999
2002-9999
2017-2021
2002-9999
2000-9999
2013-9999
2014-9999
2014-2021
2020-2022
2014-9999
2002-9999
2015-9999
2001-9999
2010-9999
2020-9999
2015-9999
2019-9999
2013-9999
2013-9999
2007-9999
2013-9999
2015-9999
2017-9999
2014-9999
2020-9999
2020-2026
2020-9999
2011-9999
2016-9999
2016-9999
2016-9999
2015-9999
2021-9999
2021-9999
2011-9999
2016-9999
2016-9999
2016-9999
2015-9999
2021-9999
2021-9999
2011-9999
2016-9999
2016-9999
2016-9999
2014-9999
2015-9999
2021-9999
2021-9999
2010-9999
2008-9999
2001-9999
1996-9999
1996-9999
2013-9999
2021-9999
2016-9999
2015-2024
2021-2025
2022-9999
2016-9999
2013-9999
2006-9999
2013-9999
2020-9999
2001-9999
2020-9999
2011-9999
Monitoring frequency
3-monthly
Yearly
Monthly
Other
3-monthly
Continually
6-monthly
Other
Unknown
Other
Unknown
Continually
Unknown
3-yearly
2-yearly
Continually
Yearly
Other
3-monthly
Yearly
Yearly
Yearly
6-yearly
6-monthly
Continually
Unknown
6-yearly
6-yearly
3-monthly
Yearly
Yearly
Yearly
Continually
Continually
As needed
3-monthly
Yearly
Yearly
Yearly
Continually
Continually
As needed
3-monthly
Yearly
Yearly
Yearly
Yearly
Continually
Continually
As needed
Yearly
3-monthly
3-monthly
Continually
Continually
Yearly
3-yearly
Yearly
Continually
Continually
Yearly
Yearly
3-monthly
As needed
3-monthly
As needed
Other
Unknown
6-monthly
Monitoring type
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote surveillance
  • Remote flight imagery
  • Administrative data collection
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Administrative data collection
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • Other
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • Administrative data collection
  • Administrative data collection
  • In-situ sampling land/beach
  • Visual observation
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • Administrative data collection
  • In-situ sampling land/beach
  • Visual observation
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • Administrative data collection
  • In-situ sampling land/beach
  • Visual observation
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling offshore
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling offshore
  • Administrative data collection
  • Administrative data collection
  • Ecological modelling
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
  • Remote flight imagery
  • Visual observation
  • In-situ sampling offshore
  • Administrative data collection
  • In-situ sampling coastal
  • Remote surveillance
  • Administrative data collection
  • Administrative data collection
  • Visual observation
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • Visual observation
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • In-situ sampling land/beach
  • In-situ sampling coastal
  • In-situ sampling offshore
  • In-situ sampling coastal
  • In-situ sampling offshore
Monitoring method
  • Other monitoring method
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Other monitoring method
  • Other monitoring method
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • OSPAR Coordinated Environmental Monitoring Programme (CEMP) Guidelines for Monitoring and Assessment of plastic particles in stomachs of fulmars in the North Sea area
  • SISP 15 - Manual of the IBTS North Eastern Atlantic Surveys
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • OSPAR Coordinated Environmental Monitoring Programme (CEMP) Guidelines for Monitoring and Assessment of plastic particles in stomachs of fulmars in the North Sea area
  • Other monitoring method
  • HELCOM Guidelines for monitoring beach litter
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • SISP 15 - Manual of the IBTS North Eastern Atlantic Surveys
  • SISP 7 - BITS Manual for the Baltic International Trawl Surveys
  • Other monitoring method
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • SISP 9 Manual for International Pelagic Surveys (IPS) - Version 1.00
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • International bottom trawl survey in the Mediterranean Manual (Version 9)
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR Coordinated Environmental Monitoring Programme (CEMP) Guidelines for Monitoring and Assessment of plastic particles in stomachs of fulmars in the North Sea area
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • Manual for the Offshore Beam Trawl Surveys (WGBEAM)
  • NEAFC: Recording of Catch and Fishing Effort
  • NEAFC: Vessel Monitoring System
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • SISP 15 - Manual of the IBTS North Eastern Atlantic Surveys
  • SISP 6 - Manual for mackerel and horse mackerel egg surveys, sampling at sea
  • SISP 9 Manual for International Pelagic Surveys (IPS) - Version 1.00
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • OSPAR Coordinated Environmental Monitoring Programme (CEMP) Guidelines for Monitoring and Assessment of plastic particles in stomachs of fulmars in the North Sea area
  • OSPAR Coordinated Environmental Monitoring Programme (CEMP) Guidelines for Monitoring and Assessment of plastic particles in stomachs of fulmars in the North Sea area
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • ICCAT Manual: Data for Assessment and Research
  • Other monitoring method
  • Other monitoring method
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR Coordinated Environmental Monitoring Programme (CEMP) Guidelines for Monitoring and Assessment of plastic particles in stomachs of fulmars in the North Sea area
  • Other monitoring method
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Guidance on Monitoring of Marine Litter in European Seas [note: to be updated with specific guidance for beaches, water, seabed and microlitter when available from TG Litter]
  • Other monitoring method
  • HELCOM Guidelines for monitoring beach litter
  • OSPAR CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
  • Other monitoring method
  • Other monitoring method
  • OSPAR CEMP Guidelines on Litter on the Seafloor
  • Other monitoring method
  • SISP 10 - Manual for the International Bottom Trawl Surveys, Revision IX
  • WFD Guidance document n.° 7 - Monitoring under the Water Framework Directive (monitoring framework)
Monitoring method other
Counting the number of marine litter items on a selected stretch of beach following the Guideline for monitoring marine litter on the beaches in the OSPAR Maritime Area. http://www.ospar.org/documents/dbase/decrecs/agreements/10-02e_beachlitter%20guideline_english%20only.pdf
Following OSPAR-EcoQO guidelines (http://qsr2010.ospar.org/media/assessments/EcoQO/EcoQO_P01-16_complete.pdf)
|| MP_051 || Investigatives Monitoring im Rahmen von FuE-Vorhaben
|| MP_066 ||
|| MP_067 ||
|| MP_068 ||
|| MP_071 || EU-TG ML (2013), Guidance on Monitoring of Marine Litter in European Sea
|| MP_073 || -- #Investigatives Monitoring im Rahmen von FuE-Vorhaben, #Videobefliegungen der deutschen Nord- und Ostsee mit einem HiDef-System, #Auswertung der Videos am Bildschirm nach einer Kategorisierung von Cheshire et al. (2009), #Erfassung treibenden Mülls im Rahmen von Schweinswalbefliegungen der deutschen Nord- und Ostsee, #Zählen der Müllteile und Zuordnung zu fischereibezogenem Müll und anderem Müll, #Erfassung von Müllteilen > 10 cm.
|| MP_262 || standardisierte Zählung von Paraffinen und anderen Persistent Floatern an der Küste und in der Oberflächenschicht der Wassersäule
|| MP_070 || Investigatives Monitoring im Rahmen von FuE-Vorhaben
Det bliver i den kommende programperiode undersøgt om det er fordelagtigt at bruge andre indikator-organismer end sild og torsk eller evt. inddrage tilfældige forekomster (f.eks. strandinger af døde dyr) til overvågning af affald i biota. Det er hensigten at affald i biota overvåges min. to gange i programperioden.
https://bios.au.dk/fileadmin/bioscience/Fagdatacentre/MarintFagdatacenter/TekniskeAnvisninger2011_2015/TA_M29_Marint_affald_ver1.pdf
Technical details are described in the current version of the survey manual (ICES 2012: Manual for the International Bottom Trawl Surveys. Series of ICES Survey Protocols. SISP 1-IBTS. 68 pp. http://datras.ices.dk/Documents/Manuals/) or http://ices.dk/sites/pub/Publication%20Reports/ICES%20Survey%20Protocols%20(SISP)/SISP1-IBTSVIII.pdf
https://fiskeristyrelsen.dk/erhvervsfiskeri/indberetning-og-foering-af-logbog/tabte-redskaber/
Metoden er beskrevet i den relevante rapport på siden: https://mst.dk/natur-vand/overvaagning-af-vand-og-natur/hav-og-fjord/rapporter/
https://mst.dk/natur-vand/overvaagning-af-vand-og-natur/hav-og-fjord/rapporter/
La metodología utilizada para la realización de las campañas puede consultarse en el documento "Programa de vigilancia de basuras marinas en playas. Protocolo de muestreo, MAGRAMA 2017".
En las campañas anuales llevadas a cabo por el IEO, como PELACUS o MEDIAS en paralelo al resto de actividades que se llevan a cabo, se realizan monitoreos mediante censos visuales de la presencia y composición de las basuras flotantes en las estaciones de muestreo definidas con los/as jefes/as de campañas a lo largo de su recorrido. En el caso de recogida y seguimiento de basuras flotantes a lo largo del litoral de la demarcación Estrecho-Alborán se podrían utilizar embarcaciones de entre 5-10 metros de eslora con brazos hidráulicos para la obtención de los residuos flotantes tal como se hace en algunas regiones del Mediterráneo español. Con este sistema de recogida es posible obtener el peso húmedo de las distintas tipologías de basuras flotantes (plásticos, maderas, algas, materia orgánica y otros), así como el porcentaje relativo de cada fracción.
En cuanto a la recogida de datos de iniciativas de pesca de basura, actualmente el MITERD, en el marco del proyecto INTEMARES, va a desarrollar unas directrices nacionales sobre pesca de basura, que incluirá un protocolo estandarizado de toma de datos, así como una base de datos a nivel nacional para recoger la información obtenida por las iniciativas existentes y las que surjan en el futuro.
Para el muestreo de micropartículas en superficie y columna de agua se aplicauna adaptación de la metodología recogida en Viršek et al., (2016). En las estaciones de muestreo determinadas con los/as jefes/as de campaña se realizan pescas de arrastre superficiales con manta trawl (330 μm) de una duración aproximada de 30 minutos y a una velocidad constante de 2-3 nudos, siempre y cuando las condiciones meteorológicas sean favorables. En el caso de que la red se sature de material orgánico e inorgánico, este tiempo de navegación se reduce. La manta trawl se tira por popa o por estribor/babor a una distancia aproximada de 3-4 metros de la embarcación evitando la zona de turbulencias en el interior de la estela del barco y soltando suficiente cabo de manera que la mitad de la estructura metálica de la manta trawl quede sumergida en el agua y la otra mitad flotando en superficie. Si el muestreo se realiza por popa sonnecesarios unos 50 metros de cabo, y si se realiza por estribor/babor unos 10 metrosde cabo. Esnecesario anotar en la hoja de datos las coordenadas iniciales/finales del GPS y la hora inicial/final.Los microplásticos se caracterizan de forma visual en base a su forma, tamaño y color. Se realizan también identificaciones químicas de los polímeros en un pequeño porcentaje de microplásticos (entre un 5-10 %). Las técnicas de identificación de microplásticos están avanzando considerablemente y se prevé su incorporación en la medida de lo posible a las tareas del programa de seguimiento.
Las muestras de sedimentos marinos superficiales se obtienen mediante el uso de una draga Box Corer. De la muestra se lleva a cabo una caracterización visual del sedimento, incluyendo los parámetros de color, olor, textura, presencia/ausencia de organismos macrobentónicos o restos vegetales. Posteriormente, se lleva a cabo un análisis de granulometría, y otras variables como contenido en materia orgánica y concentración de metales traza, compuestos orgánicos persistentes e hidrocarburos aromáticos policíclicos en la fracción total (< 2 mm) del sedimento. Dentro de este marco, sería factible que se llevara a cabo también la caracterización física de los microplásticos (cantidad, forma, tamaño, volumen, color y estado) siguiendo los protocolos desarrollados en el seno del BASEMAN project (JPI Oceans).
En cada una de las playas incluidas en el programa, se toman 5 muestras de arena. Cuando la playa pertenece también al programa BM-1 “basuras en playas”, las muestras se toman dentro del transecto de muestreo de 100 metros utilizado en el mismo. Las estaciones se posicionan con ayuda de GPS en el centro, los extremos y 1/4 de su longitud en cada orientación, en todos los casos se utiliza un marco de 50 x 50 cm que se dispone sobre la marca en la arena correspondiente a la línea de la última pleamar. Cuando las playas no están incluidas en el programa BM-1, las muestras se toman a idénticos intervalos de longitud que en el resto de las playas, sobre un sector determinado de las mismas. Dentro del mencionado marco y con la ayuda de una paleta metálica se recoge el primer centímetro de la superficie de la arena y se trasvasa a un recipiente de la capacidad adecuada y perfectamente identificado con la referencia de la muestra. Las muestras brutas son transportadas para su procesado íntegro en el laboratorio, donde son secadas y tamizadas a través de dos tamices de 5 y 1 mm cada uno. Posteriormente se lleva a cabo una separación por flotación en solución saturada de NaCl. Para facilitar el recuento de las partículas de tamaño inferior a 1 mm, antes de la filtración por membrana y paso a placa Petri para el recuento de partículas, se realiza una tinción con Rojo de Nilo, en el recuento en microscopio se utiliza una fuente de iluminación azul de 450-510 nm2. Esta tinción hace imposible su clasificación por color. El recuento de las partículas de microplásticos retenidas en las dos membranas de filtración correspondientes a cada muestra se realiza mediante una lupa binocular con un ocular micrométrico acoplado que permite la medida del tamaño de las partículas. Dada la metodología analítica utilizada, la cantidad de micropartículas detectada en las muestras se puede expresar tanto en función de la masa (por kg de arena) como por superficie (por m2 de playa). Para ambas fracciones, las partículas también se clasifican por tamaños, y por forma, siguiendo en este último caso, los mismos criterios de clasificación recomendados por el Subgrupo Técnico de Basuras Marinas de la DMEM (TSG-ML) (http://mcc.jrc.ec.europa.eu/documents/201702074014.pdf). En el caso de las fracción superior a 5mm también se expresan los resultados en masa: mg/kg o mg/m2, y se lleva a cabo una clasificación de las partículas por color.
En colaboración con entidades organizadoras de acciones de voluntariado a nivel nacional, se ha desarrollado y acordado una tarjeta de toma de datos en campo que se ha publicado para su libre uso: https://www.miteco.gob.es/es/costas/temas/proteccion-medio-marino/formatopdfimprimible_tcm30-437422.pdf Se prevé la incorporación de una tarjeta similar dirigida a las acciones de voluntariado con buceadores en fondos someros. Actualmente la más ampliamente utilizada es la desarrollada por el proyecto MARNOBA: https://vertidoscero.com/herramientas-marnoba/ (“Formulario de objetos MARNOBA fondos”). La información obtenida se considera complementaria a la obtenida en los programas BM-1 y BM-3. Actualmente, diversas entidades de voluntariado, así como el proyecto MARNOBA, envían anualmente al MITERD los datos en formato ficha (brutos) o informe (procesados). La información que se recibe procesada se publica en los informes anuales del programa BM-1, como información complementaria. El MITERD está desarrollando un Sistema de Información del Mar, INFOMAR, donde podrán recibirse automáticamente y almacenarse los datos procedentes de ciencia ciudadana junto con todos aquellos datos de los programas de seguimiento de las estrategias marinas, para su mejor tratamiento. Como mejoras futuras, se prevé la puesta en marcha de un registro y declaración responsable que contenga información básica sobre organizadores, número de voluntarios y localización de las acciones de voluntariado para evitar interacciones no deseadas con el programa de seguimiento BM-1. Se prevé también facilitar un retorno a los proveedores de datos en formato de informe.
En febrero de 2017 se dio comienzo al proyecto INDICIT, con financiación de la Comisión Europea, cuyo principal objetivo es el desarrollo del seguimiento de basuras en biota, con especial hincapié en las tortugas marinas como indicadoras. Actualmente está desarrollándose INDICIT II (2019-2021). El consorcio, compuesto por 12 socios de 8 países (Francia, Grecia, Italia, España, Portugal, Túnez, Turquía y Reino Unido) desarrolló en INDICIT I el indicador de ingestión de macro-basura por tortugas y su protocolo estandarizado, que incluye tanto tortugas vivas como muertas, así como la identificación varios tipos de polímeros artificiales (pellets, film, fragmentos, filamentos, foam) a través de análisis de heces o necropsias: https://indicit-europa.eu/indicit-documents/(INDICIT – Standard protocol Ingestion debris sea turtles – EN – Sept 2018). Este programa tiene por objeto aplicar este protocolo de forma rutinaria a través de las redes de varamientos y los centros de recuperación de fauna silvestre que gestionan las CCAA litorales. Para ello, este protocolo se incluirá en el protocolo general de las redes de varamientos. De forma adicional, INDICIT II está desarrollando el indicador de enmallamiento de organismos (tortugas, mamíferos y aves) en basuras marinas, así como el indicador de ingestión de microplásticos (tortugas y peces). Una vez el proyecto obtenga protocolos estandarizados para estos indicadores se valorará su incorporación a este programa de seguimiento rutinario. Existe potencialidad en la exploración de vías alternativas de toma de datos, como son: • Otros proyectos que están tomando datos en tiburones peregrinos o cetáceos, con los que se podría acordar un protocolo mínimo. • Las campañas de seguimiento de contaminantes en mejillón y salmonete de fango del IEO (campaña IBERIANMULLUS). • Las campañas de recursos pesqueros MEDIAS y MEDITS: salmonetes de fango (Mullus barbatus), salmonetes de roca (Mullus surmuletus) y la boga (Boops boops), especies validas e indicadas como bioindicadoras de plásticos en el medio marino. Para la determinación de ingesta de plásticos en biota, durante el muestreo biológico de las respectivas campañas y muestreos biológicos contemplados en la recopilación de datos biológicos del PNDB para la demarcación levantino-balear, se obtendrá el tracto digestivo y estómago de un mínimo de 15 individuos por especie objetivo (salmonetes, boga), así como 15 individuos enteros (tejido blando) de mejillones
Se recopilará la información entre las unidades administrativas competentes en cada uno de los indicadores asociadas a los objetivos.
Respecto a las macrobasuras en playas, se utilizan los datos estacionales de basuras marinas de un transecto de 100 m procedentes del programa de seguimiento BM1. Se consideran los resultados considerando el “top X” (objetos más frecuentes) de las tipologías de objetos, entendido como el que representa el 80% de los objetos encontrados. En el establecimiento de los orígenes de las macrobasuras en playas según los objetos más frecuentes (top X) se ha seguido lo indicado por el Convenio OSPAR, que, a través de su Grupo de Trabajo de Basuras Marinas (ICG-ML), tiene establecida una metodología consistente en la asignación de cada tipo de basura de los contemplados en el muestreo a cada uno de los 5 siguientes grupos de orígenes: pesca, transporte marítimo, turismo, instalaciones sanitarias y otros. En esta última categoría se incluyen aquellos objetos cuyo origen no pueda ser asignado a alguna de las anteriores categorías o aquellos que puedan corresponderse con más de una fuente. Además, se han redefinido las categorías establecidas por OSPAR para adecuarlas a las actividades listadas en el Cuadro 2b del Anexo III de la DMEM. Los datos de basuras recogidas y del tráfico de buques en los puertos de interés general proceden de Puertos del Estado.
Ce sous-programme repose sur des dispositifs de collecte (e.g. base de données, règlement, contrôle, étude d'impact, enquête, infrastructure de données...) permettant de fournir régulièrement un ou des jeux de données relatifs aux activités, aux usages ou aux politiques publiques. Le dispositif de collecte utilisé fournit des données sur la "quantité totale de déchets des engins de pêche contenant du plastique (filière aqaucole et filière pêche)".
Ce sous-programme repose sur des dispositifs de collecte (e.g. base de données, règlement, contrôle, étude d'impact, enquête, infrastructure de données...) permettant de fournir régulièrement un ou des jeux de données relatifs aux activités, aux usages ou aux politiques publiques. Le dispositif de collecte utilisé fournit des données sur la "quantité totale de déchets des engins de pêche contenant du plastique (filière aqaucole et filière pêche)".
Ce sous-programme repose sur des dispositifs de collecte (e.g. base de données, règlement, contrôle, étude d'impact, enquête, infrastructure de données...) permettant de fournir régulièrement un ou des jeux de données relatifs aux activités, aux usages ou aux politiques publiques. Le dispositif de collecte utilisé fournit des données sur la "quantité totale de déchets des engins de pêche contenant du plastique (filière aqaucole et filière pêche)".
MSFD GES Technical Subgroup on Marine Litter (TSG-ML). Monitoring Guidance for Marine Litter in European Seas. DRAFT REPORT, July 2013. International Council for the Exploration of the Sea (ICES) 2020. Manual for the North Sea International Bottom Trawl Surveys. Series of ICES Survey Protocols SISP 10-IBTS 10, Revision 11. 102 pp
Microplastics were not previously covered in the MSFD monitoring programme. On the basis of technical specifications and in consultation with OSPAR, Rijkswaterstaat is developing a monitoring method and monitoring network survey for microplastics in sediment. The method is expected to be operational from the beginning of 2021. International coordination takes place under the auspices of OSPAR; to which the MSFD monitoring programme is linked as closely as possible. In recent years, a lot has been learned about the presence, the analysis and the effects of microplastics in national and international research programmes, including JPI Oceans, EU programmes and in the context of regional marine sea conventions. The OSPAR microplastic expert group is currently working to construct OSPAR CEMP guidelines for monitoring of microplastics in marine sediment. The finalization of these CEMP guidelines is expected no sooner than in 2022, because many countries are still gaining experience with this new type of monitoring. With these CEMP guidelines, a common OSPAR indicator for microplastics in marine sediment will be established. The monitoring of emissions of microplastics is still in the research phase. Various long-term research programmes are underway in the Netherlands, including the TRAMP project financed by the Technology Foundation STW.58 Steps will be taken in the coming years to develop a first monitoring programme for microplastics in fresh water, primarily designed to determine and model the microplastics mass load.
Chambault, P., Vandeperre, F., Machete, M., Lagoa, J. C., & Pham, C. K. (2018). Distribution and composition of floating macro litter off the Azores archipelago and Madeira (NE Atlantic) using opportunistic surveys. Marine environmental research, 141, 225-232
Vandeperre, F., Parra, H., Machete, M. 2020. A pesca com palangre de superfície nos Açores. Relatório do projeto COSTA – COnsolidating Sea Turtle conservation in the Azores, p.10
A metodologia deste programa encontra-se descrita em GAMPA (2021).
O presente programa de monitorização visa o acompanhamento da implementação das disposições do DL 102/2020 relativas à receção de resíduos e medidas de controlo, monitorização e redução do lixo marinho em Portos comerciais, Portos de pesca e Marinas, através das seguintes atividades: 1. Identificação dos portos e/ou fundeadouros não abrangidos pela obrigatoriedade de submissão do plano de receção e gestão de resíduos ao abrigo do referido DL; 2. Execução de um projeto-piloto de monitorização de lixo marinho em bacias portuárias de portos comerciais, a selecionar, que inclui: a. Macrolixo na superfície: Recolha bi-anual e análise do lixo recolhido à superfície e coluna de água das áreas portuárias, com recurso a dispositivos para recolha de lixo à superfície b. Macrolixo nos fundos: Levantamento geofísico de hotspots de acumulação de lixo marinho nos fundos, com recurso a equipamento multifeixe e periodicidade anual; c. Recolha e monitorização de poliestireno expandido nos portos através da implementação das melhores práticas definidas no projeto OceanWise; 3. Definição de um protocolo, adaptado às diferentes tipologias de portos e marinas, para receção e monitorização de resíduos provenientes de navios e do lixo marinho recolhido nas respetivas bacias portuárias, incluindo o plano, a coluna de água e o solo marinho; 4. Realização de ações de formação.
INDICIT (2018). Monitoring marine litter impacts on sea turtles. Protocol for the collection of data on ingestion and entanglement in the loggerhead turtle (Caretta caretta Linnaeus, 1758). Deliverable D2.6 of the European project "Implementation of the indicator of marine litter impact on sea turtles and biota in Regional Sea conventions and Marine Strategy Framework Directive areas" (indicit-europa.eu). Grant agreement 11.0661/2016/748064/SUB/ENV.C2. Bruxelles. 22 pp Bessa, F., Frias, J., Kögel, T., Lusher, A., Andrade, J. M., Antunes, J., Sobral, P., Pagter, E., Nash, R., O’Connor, I., Pedrotti, M. L., Kerros, M. E., León, V., Tirelli, V., Suaria, G., Lopes, C., Raimundo, J., Caetano, M., Gago, J., Viñas, L., Carretero, O., Magnusson, K., Granberg, M., Dris, R., Fischer, M., Scholz-Böttcher, B., Muniategui, S., Grueiro, G., Fernández, V., Palazzo, L., de Lucia, A., Camedda, A., Avio, C. G., Gorbi, S., Pittura, L., Regoli, F., Gerdts, G. (2019) Harmonized protocol for monitoring microplastics in biota. JPI-Oceans BASEMAN project. 30 pp. DOI: 10.13140/RG.2.2.28588.72321/1
Filgueras, A., Gago, J., Pedrotti, M.L., Suaria, G., Tirelli, V., Andrade, J., P.G.L. Frias, J., Nash, R., O’Connor, I., Lopes, C., Caetano, M., Raimundo, J., Carretero, O., Vinas, L., Antunes, J., Bessa, F., Sobral, P., Goruppi, A., Aliani, S., Palazzo, L., de Lucia, G.A., Camedda, A., Muniategui, S., Gruceiro, G., Fernandez, V. and Gerdts, G., (2019). Standardised protocol for monitoring microplastics in seawater JPI-Oceans BASEMAN project. 33 pp. 10.13140/RG.2.2.14181.45282 Frias, J., Pagter, E., Nash, R., O’Connor, I., Carretero, O., Filgueiras, A., Gago, J., Antunes, J., Bessa, F., Sobral, P., Goruppi, A., Tirelli, V., Pedrotti, M.L., Suaria, G., Aliani, S., Lopes, C., Caetano, M., Raimundo, J., Palazzo, L., de Lucia, G.A., Camedda, A., Muniategui, S., Gruceiro, G., Fernandez, V., Andrade, J., Dris, R., Laforsch, C., Scholz-Böttcher, B.M. and Gerdts, G., (2018). Standardised protocol for monitoring microplastics in sediments. JPI-Oceans BASEMAN project.10.13140/RG.2.2.36256.89601/1 Herrera, A., Raymond, E., Martínez, I., Álvarez, S., Canning-Clode, J., Gestoso, I., Pham, C., Ríos, N., Rodríguez, Y. & Gómez, M. (2020). First evaluation of neustonic microplastics in the Macaronesian region, NE Atlantic. Marine pollution bulletin, 153, 110999.
https://www.hsr.se/sites/default/files/appendix1_measurement_method.pdf
No method is yet decided. The methods used to this day are: Manta trawl and pump for sea surface Sediment cores for sediment.
http://ices.dk/sites/pub/Publication%20Reports/Expert%20Group%20Report/HAPISG/2018/01%20WGML%20-%20Report%20of%20the%20Working%20Group%20on%20Marine%20Litter.pdf
Quality control
DelayedValidation
Unknown
Unknown
|| MP_051 || Investigatives Monitoring im Rahmen eines FuE-Vorhaben. QS verfolgt nach internen Standards.
|| MP_066 || OSPAR Beach-Litter Monitoring Guidelines CEMP Guidelines for monitoring marine litter washed ashore and/or deposited on coastlines (beach litter)
|| MP_067 || OSPAR EcoQO OSPAR Commission 2009: Handbook for the application of Ecological Quality Objectives in the North Sea. Second edition, Publication 307/2009.
|| MP_068 || Verwendung gemeinsamer Probenahmeprotokolle (ICES)
|| MP_071 || Investigatives Monitoring im Rahmen von FuE-Vorhaben. QS erfolgt nach internen Standards.
|| MP_073 || Investigatives Monitoring im Rahmen von FuE-Vorhaben. QS erfolgt nach internen Standards.
|| MP_262 || abgestimmte Methodik zwischen Bund und Ländern
|| MP_070 || Investigatives Monitoring im Rahmen von FuE-Vorhaben. QS erfolgt nach internen Standards.
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 ...
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 a...
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 a...
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 a...
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 a...
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 a...
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 a...
Otros estándares: cursos periódicos de formación de observadores Otros controles de calidad: validación de los datos recogidos por observadores.
Data are monitored by IEO researchers.
Other quality checks: That applied by the competent authorities in the execution of the activity. Data are monitored by IEO research staff.
Data are monitored by IEO researchers.
Data are monitored by IEO researchers.
Además de los controles de calidad especificados en los protocolos de muestreo y análisis en laboratorio, el Laboratorio de Calidad del Medio Marino del Centro de Estudios y Experimentación de Obras Públicas está preparando su participación en un programa europeo de evaluación para laboratorios e...
Otros estándares: el aplicado por las entidades de voluntariado en la ejecución de la actividad. Otros controles de calidad: el aplicado por las entidades de voluntariado en la ejecución de la actividad.
el aplicado por las redes de varamientos y centros de recuperación en la ejecución de la actividad
Internal controls will be implemented to review documentation by the Responsible Authority (MITERD, through the Subdirectorate-General for the Protection of the Sea).
Other quality checks: That applied by the competent authority in the execution of the activity.
Les données sont contrôlées annuellement selon la méthode OSPAR (voir OSP-014).
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées.
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Les données sont également contrôlées annuellement selon la méthode OSPAR (voir OSP-015).
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées.
Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Ifremer dispose de la certification ISO 9001, tous sites et toutes activités.
Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Ifremer dispose de la certification ISO 9001, tous sites et toutes activités.
La méthodologie et le contrôle qualité est en cours de stabilisation pour ce nouveau sous-programme dédié aux suivis des activités, usages et politiques publiques des espaces maritimes et littoraux (données administratives). À terme, ce sous-programme a pour ambition d'intégrer des dispositifs ré...
Les données sont contrôlées annuellement selon la méthode OSPAR (voir OSP-014).
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées.
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Les données sont également contrôlées annuellement selon la méthode OSPAR (voir OSP-015).
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées.
Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Ifremer dispose de la certification ISO 9001, tous sites et toutes activités.
Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Ifremer dispose de la certification ISO 9001, tous sites et toutes activités.
La méthodologie et le contrôle qualité est en cours de stabilisation pour ce nouveau sous-programme dédié aux suivis des activités, usages et politiques publiques des espaces maritimes et littoraux (données administratives). À terme, ce sous-programme a pour ambition d'intégrer des dispositifs ré...
Les données sont contrôlées annuellement selon la méthode OSPAR (voir OSP-014).
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées.
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités. Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Les données sont également contrôlées annuellement selon la méthode OSPAR (voir OSP-015).
Ifremer (opérateur de surveillance) dispose de la certification ISO 9001, tous sites et toutes activités.Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées.
Les données sont contrôlées annuellement selon la méthode OSPAR (voir OSP-017). Les données bancarisées dans la BD Oiseaux (OFB) sont également contrôlées et qualifiées.
Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Ifremer dispose de la certification ISO 9001, tous sites et toutes activités.
Les données bancarisées dans BD DALI (Quadrige ; IFREMER) sont contrôlées et qualifiées. Ifremer dispose de la certification ISO 9001, tous sites et toutes activités.
La méthodologie et le contrôle qualité est en cours de stabilisation pour ce nouveau sous-programme dédié aux suivis des activités, usages et politiques publiques des espaces maritimes et littoraux (données administratives). À terme, ce sous-programme a pour ambition d'intégrer des dispositifs ré...
ICES2020. Manual for the North Sea International Bottom Trawl Surveys. Series of ICES Survey Protocols SISP 10-IBTS 10, Revision 11. 102 pp. http://doi.org/10.17895/ices.pub.7562
CEMP Guidelines for marine monitoring and assessment of beach litter
Monitoring of litter on the beach is carried out by the North Sea Foundation on behalf of RWS. The measurements are carried out by experienced employees according to strict OSPAR protocols. The results are processed annually into an extensive report with static analyzes and trend calculations. http://publicaties.minienm.nl/download-bijlage/96367/bm-18-15-ospar-beach-litter-monitoring-in-the-netherlands-2012-2017-annual-report.pdf
The monitoring of plastics in petrels is carried out by Wageningen Marine Research according to an internationally agreed method. The results are processed annually into an extensive report with static analysis and trend calculations. Ongoing data quality by OSPAR-ICG-ML and OSPAR secretariat.
The monitoring of plastics in petrels is carried out by Wageningen Marine Research according to an internationally agreed method. The results are processed annually into an extensive report with static analysis and trend calculations. Ongoing data quality by OSPAR-ICG-ML and OSPAR secretariat.
Monitoring of litter on the seabed is part of the IBTS survey and is coordinated by ICES. This monitoring is relatively new and not yet fully developed, which means that the quality of the collected data can be further improved.
The monitoring of microplastics is still under development. Data quality control has not yet been organized for this monitoring.
A qualidade dos dados será garantida pelas entidades competentes na implementação deste programa de monitorização, com o apoio das equipas científicas que efetuam a análise dos dados recolhidos.
Os relatórios são digitalizados e o coordenador faz análises de qualidade de controlo dos dados por cruzamento com dados de descargas, diários de pesca e pela utilização de relações peso-comprimento.
Este programa tem pressupostos para implementação de controlo de qualidade (consistência, precisão e confiança) para responder aos requisitos de avaliação e gestão em GAMPA (2021).
A qualidade será assegurada pela validação da DGRM de acordo com o DL 102/202, de 9 de dezembro, dos dados submetidos na plataforma a disponibilizar.
Aplica-se o método de controlo utilizado pelas redes de arrojamento e equipas científicas que analisam as amostras.
Os dados recolhidos será validados por equipas especializadas do grupo de trabalho para o beach litter da OSPAR (BLEG).
A qualidade dos dados será garantida pelas entidades competentes na implementação deste programa de monitorização, com o apoio das equipas científicas que efetuam a análise dos dados recolhidos.
A qualidade dos dados será garantida pelas entidades competentes na implementação deste programa de monitorização, com o apoio das equipas científicas que efetuam a análise dos dados recolhidos.
A qualidade dos dados será garantida pelas entidades competentes na implementação deste programa de monitorização, com o apoio das equipas científicas que efetuam a análise dos dados recolhidos. Serão utilizados pontos de controlo.
Intercalibration exercises and workshops are conducted to practice and compare the categorization of litter
As the risk of contamination of microlitter samples is high, blank samples are always used and handled in the same way as other samples in order to be able to take into account any contamination from the time the sample was collected until it was analyzed. Since samples are processed by breaking down organic material before analysis, a check to control if plastic particles are affected by the treatment is carried out by exposing a selection of plastic particles and plastic fiber for the same treatment. In the sampling comparison in 2017, the methods pump and trawl were compared, both of which proved to have advantages and disadvantages. The advantage of the pump is that the volume of water collected is accurate, while the volume of filtered water in the trawl is more uncertain. With the trawl, however, more water can be filtered in a shorter time, which means that more particles are collected, which provides a more reliable result. The mesh size of the trawl is hydrodynamically limited to about 300 µm while the pump can be used down to 50 µm. The ongoing development of monitoring methods takes into account uncertainties in the data, and the goal is to develop a reliable method that provides reliable results that can be used for monitoring environmantal status and effects of measures.
Methodology and appropriate litter categories to register have been revised at international BITS and IBTS meetings and on ICES's website there is information on litter category codes and size ranges for reporting of data to ICES's Datras database. In 2018, ICES held its first international working group meeting focusing on marine litter. The meeting resulted in, among other things, detailed advice on methodology for collecting litter and how different types of litter should be registered. Within the working group, work is also underway to produce a photo guide, as litter can look different in different sea areas. http://ices.dk/sites/pub/Publication%20Reports/Expert%20Group%20Report/HAPISG/2018/01%20WGML%20-%20Report%20of%20the%20Working%20Group%20on%20Marine%20Litter.pdf
Data management
The data is reported to OSPAR and transmitted through BMDC's Data Tracking System, which makes it publicly accessible through RBINS' metadata catalogue (http://metadata.naturalsciences.be).
Currently, all data are stored at ILVO (Smartfish). The data are uploaded to DATRAS, the survey database hosted by ICES, on a yearly basis. This database is an open access source and can be consulted through the website (www.datras.ices.dk).
The data is transmitted annually through BMDC's Data Tracking System, which makes it publicly accessible through RBINS' metadata catalogue (http://metadata.naturalsciences.be).
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
Die Bund/Länder-Arbeitsgemeinschaft Nord- und Ostsee (BLANO) erarbeitet gerade ein nationales Konzept zum Datenmanagement, um insbesondere die Berichterstattung und Umsetzung der MSRL zu unterstützen. Dabei werden bestehende Zielsysteme, wie die Datenabgabe an den ICES (für OSPAR und HELCOM), wei...
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.
The data processed are uploaded to the IEO Geographical Information System (GIS). They are pre-loaded in other applications such as EMODNET or ICES Dome.
Data are monitored by IEO research staff. These data are uploaded in applications such as ICES or other applications used internally by the IEO.
The data processed are uploaded to the IEO Geographical Information System (GIS). They are pre-loaded in other applications such as EMODNET or ICES Dome.
The data processed are uploaded to the IEO Geographical Information System (GIS). They are pre-loaded in other applications such as EMODNET or ICES Dome.
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
Marine Institute Database Nationally and ICES DATRAS database
ACCESS Database Nationally and OSPAR Beach Litter Monitoring Database
Marine Information and Data Centre
Marine Information and Data Centre
Marine Information and Data Centre
Marine Information and Data Centre
Este programa em vias de ser implementado, tem agendadas ações que permitam o armazenamento em repositórios e sistemas de armazenamento em que o acesso aos dados garantam a confidencialidade e propriedade intelectual (SCPI) da informação recolhida, analisada e processada.
Os dados recolhidos nas 3 sub-divisões são reportados no Banco de Dados de Lixo de Praia da OSPAR (https://beachlitter.ospar.org/).
All Swedish data is collected in a Swedish database run by Keep Sweden Tidy. To gain access to data, you need a password that you get by contacting Keep Sweden Tidy. Raw data can be obtained on request and selected results will be presented on the website. Data may be used freely. OSPAR data is also delivered to OSPAR regional database, no later than one month after each measurement. Keep Sweden Tidy delivers Swedish data to HELCOM and the EU when they are requested for international compilations. All Swedish data is also reported to the European database EMODnet.
Data are currently only available from the contractors who carried out the monitoring projects. There is still no national data host for microlitter, but the goal is for it to be in place when ongoing monitoring is started. Within the EU, EmodNet is being developed to also include marine litter, including microlitter.
The raw data collected is stored at SLU and updated annually. Raw data from all participating countries is also stored at ICES. At ICES, however, there are no data from the national coastal trawling.
Data access
not yet available
Related indicator/name
  • BM-flo->Basuras flotantes
  • BM-fon->Basuras en el fondo marino
  • BM-mic->Micropartículas en agua y en sedimento
  • BM-mic->Micropartículas en agua y en sedimento
  • BM-micplaya->Micropartículas de plástico en playas
  • BM-flo->Basuras flotantes
  • BM-fon->Basuras en el fondo marino
  • BM-pla->Basuras en playas
  • B.E.12., B.L.12.
  • B.N.1., B.S.1., B.C.1., B.E.1., B.L.1.
  • B.N.11., B.S.11., B.C.10., B.E.11., B.L.11.
  • B.N.12., B.S.12., B.C.11., B.E.14., B.L.14
  • B.N.13., B.S.13., B.C.12., B.E.15., B.L.15.
  • B.N.14., B.S.14., B.C.13., B.E.16., B.L.16.
  • B.N.15., B.S.15., B.C.14., B.E.17., B.L.17.
  • B.N.16., B.S.16., B.C.15., B.E.18., B.L.18.
  • B.N.2., B.S.2., B.C.2., B.E.2., B.L.2
  • B.N.4., B.S.4., B.C.3., B.E.4., B.L.4.
  • B.N.5., B.S.5., B.C.4., B.E.5., B.L.5
  • B.N.6., B.S.6., B.C.5., B.E.6., B.L.6.
  • B.N.7., B.S.7., B.C.6., B.E.7., B.L.7.
  • B.N.8., B.S.8., B.C.7., B.E.8., B.L.8.
  • B.N.9., B.S.9., B.C.8., B.E.9., B.L.9.
  • ACS-IE-MaximumSustainableYield2021
  • ACS-IE-SeabedLitter2021
  • ACS-IE-SpawingStockBiomass2021
  • ANSSE-10.1A_Skr�p_str�nder
  • ANSSE-E.1.1_Skr�p_str�nder
  • BALSE-10.1A_Skr�p_str�nder
  • BALSE-E.1.1_Skr�p_str�nder
  • ANSSE-10.1B_Skr�p_havsbotten
  • ANSSE-E.1.2_Skr�p_havsbotten
  • BALSE-10.1B_Skr�p_havsbotten
  • BALSE-E.1.2_Skr�p_havsbotten
Contact
Francis Kerckhof, Royal Belgian Institute of Natural Science (RBINS)
Bavo De Witte, Els Torreele, Institute for Agriculture, Fishery and Food research (ILVO)
Eric Stienen, Research Institute for Nature and Forest (INBO)
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
Geschäftsstelle Meeresschutz, geschaeftsstelle-meeresschutz@mu.niedersachsen.de
kregn@mst.dk
kregn@mst.dk
kregn@mst.dk
kregn@mst.dk
kregn@mst.dk
kregn@mst.dk
kregn@mst.dk
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
CHEVRIER Muriel
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
CHEVRIER Muriel
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
BEAUVAIS Sophie
CHEVRIER Muriel
Sorcha.nilongphuirt@housing.gov.ie / David.stokes@marine.ie
Sorcha.nilongphuirt@housing.gov.ie Sorcha Ni Longphuirt
https://www.informatiehuismarien.nl/uk/secundaire-navigatie/contact/
https://www.informatiehuismarien.nl/uk/secundaire-navigatie/contact/
https://www.informatiehuismarien.nl/uk/secundaire-navigatie/contact/
https://www.informatiehuismarien.nl/uk/secundaire-navigatie/contact/
Subdivisão da Madeira: Secretaria Regional de Mar e Pescas/Direção Regional do Mar (SRMar/DRM); Agência Regional para o Desenvolvimento da Investigação, Tecnologia e Inovação/Centro de Ciências do Mar e do Ambiente (ARDITI/MARE) Subdivisão dos Açores: Direção Regional dos Assuntos do Mar (DRAM), Secretaria Regional do Mar e Pescas (SRMP)
IMAR - Instituto do Mar. Departamento de Oceanografia e Pescas Subdivisão dos Açores: Secretaria Regional do Mar e Pescas / Direção Regional dos Assuntos do Mar/Direção Regional das Pescas (SRMP/DRAM/DRP)
Universidade dos Açores. Centro I&D Okeanos IMAR - Instituto do Mar. Departamento de Oceanografia e Pescas Direção Regional dos Assuntos do Mar (DRAM) / Direção Regional das Pescas(DRP)/ Secretaria Regional do Mar e das Pescas (SRMP)
Direção-Geral dos Recursos Naturais, Segurança e Serviços Marítimos
Subdivisão da Madeira: Secretaria Regional de Mar e Pescas/Direção Regional do Mar (SRMar/DRM) Subdivisão dos Açores: Direção Regional dos Assuntos do Mar (DRAM), Secretaria Regional do Mar e Pescas (SRMP) Subdivisão do Continente: Agência Portuguesa do Ambiente (APA), Instituto Português do Mar e Atmosfera (IPMA)
Subdivisão da Madeira: Secretaria Regional de Ambiente, Recursos Naturais e Alterações Climáticas/Direção Regional do Ambiente e Alterações Climáticas (SRAAC/DRAAC); Secretaria Regional de Mar e Pescas/Direção Regional do Mar (SRMar/DRM) Subdivisão dos Açores: Direção Regional dos Assuntos do Mar (DRAM), Secretaria Regional do Mar e Pescas (SRMP) Subdivisão do Continente: Agência Portuguesa do Ambiente (APA), Instituto Português do Mar e Atmosfera (IPMA)
Subdivisão Madeira: Secretaria Regional de Mar e Pescas/Direção Regional do Mar/(SRMar/DRM) Subdivisão Continente: Instituto Português do Mar e da Atmosfera (IPMA) Subdivisão Açores: Direção Regional dos Assuntos do Mar (DRAM), Secretaria Regional do Mar e Pescas (SRMP)
Subdivisão da Madeira: Secretaria Regional de Mar e Pescas/Direção Regional do Mar (SRMar/DRM); Agência Regional para o Desenvolvimento da Investigação, Tecnologia e Inovação/Centro de Ciências do Mar e do Ambiente (ARDITI/MARE) Subdivisão dos Açores: Direção Regional dos Assuntos do Mar (DRAM), Secretaria Regional do Mar e Pescas (SRMP) Subdivisão do Continente: Instituto Português do Mar e da Atmosfera (IPMA), APA, I.P.
Subdivisão Madeira: Secretaria Regional de Mar e Pescas/Direção Regional do Mar (SRMar/DRM); Agência Regional para o Desenvolvimento da Investigação, Tecnologia e Inovação/Centro de Ciências do Mar e do Ambiente (ARDITI/MARE). Subdivisão Continente: Instituto Português do Mar e da Atmosfera (IPMA) Subdivisão Açores: Direção Regional dos Assuntos do Mar (DRAM), Secretaria Regional do Mar e Pescas (SRMP)
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
miljoovervakning@havochvatten.se
References
|| MP_51 || --# #--
|| MP_66 || --# OSPAR Intermediate Assessment 2017 https://oap.ospar.org/en/ospar-assessments/intermediate-assessment-2017/pressures-human-activities/marine-litter/ # https://oap.ospar.org/en/ospar-assessments/intermediate-assessment-2017/pressures-human-activities/marine-litter/ #--
|| MP_67 || --# #--
|| MP_68 || --# Kammann U, Aust M-O, Bahl H, Lang T (2018) Marine litter at the seafloor - abundance and composition in the North Sea and the Baltic Sea. Mar Pollut Bull 127:774-780 # #--
|| MP_71 || --# #--
|| MP_73 || --# #--
|| MP_262 || --# #--
|| MP_70 || --# #--
INDICIT consortium, 2018. Monitoring marine litter impacts on sea turtles. Protocol for the collection of data on ingestion and entanglement in the loggerhead turtle (Caretta caretta Linnaeus, 1758). Deliverable D2.6 of the European project "Implementation of the indicator of marine litter impact on sea turtles and biota in Regional Sea conventions and Marine Strategy Framework Directive areas" (indicit-europa.eu). Grant agreement 11.0661/2016/748064/SUB/ENV.C2. Bruxelles. 22 pp.
INDICIT consortium, 2018. Monitoring marine litter impacts on sea turtles. Protocol for the collection of data on ingestion and entanglement in the loggerhead turtle (Caretta caretta Linnaeus, 1758). Deliverable D2.6 of the European project "Implementation of the indicator of marine litter impact on sea turtles and biota in Regional Sea conventions and Marine Strategy Framework Directive areas" (indicit-europa.eu). Grant agreement 11.0661/2016/748064/SUB/ENV.C2. Bruxelles. 22 pp.
INDICIT consortium, 2018. Monitoring marine litter impacts on sea turtles. Protocol for the collection of data on ingestion and entanglement in the loggerhead turtle (Caretta caretta Linnaeus, 1758). Deliverable D2.6 of the European project "Implementation of the indicator of marine litter impact on sea turtles and biota in Regional Sea conventions and Marine Strategy Framework Directive areas" (indicit-europa.eu). Grant agreement 11.0661/2016/748064/SUB/ENV.C2. Bruxelles. 22 pp.
Van Hal R. (2019) Dutch seafloor litter monitoring North Sea. International Bottom Trawl Survey 2019. Wageningen Marine Research, IJmuiden.
OSPAR (2018) Proposal for a candidate indicator on micro litter in sediments. Accepted by EIHA Committee.
MM, SRMCT, SRAAC (2020). Estratégia Marinha: relatório do 2º ciclo. Ministério do Mar Secretaria Regional do Mar, Ciência e Tecnologia, Açores, e Secretaria Regional de Ambiente, Recursos Naturais e Alterações Climáticas, Madeira. Março de 2020. (https://www.dgrm.mm.gov.pt/web/guest/as-pem-diretiva-quadro-estrategia-marinha)
Vandeperre, F., Parra, H., Machete, M. 2020. A pesca com palangre de superfície nos Açores. Relatorio do projeto COSTA – COnsolidating Sea Turtle conservation in the Azores, p.10
GAMPA (2021) MoniCO ‐ Programa de Monitorização de Recursos e Ambientes Costeiros dos Açores. Relatório técnico 1.2 do programa MoniCO. IMAR/Okeanos, 77 pp
MM, SRMCT, SRAAC (2020). Estratégia Marinha: relatório do 2º ciclo. Ministério do Mar Secretaria Regional do Mar, Ciência e Tecnologia, Açores, e Secretaria Regional de Ambiente, Recursos Naturais e Alterações Climáticas, Madeira. Março de 2020. (https://www.dgrm.mm.gov.pt/web/guest/as-pem-diretiva-quadro-estrategia-marinha)
MM, SRMCT, SRAAC (2020). Estratégia Marinha: relatório do 2º ciclo. Ministério do Mar Secretaria Regional do Mar, Ciência e Tecnologia, Açores, e Secretaria Regional de Ambiente, Recursos Naturais e Alterações Climáticas, Madeira. Março de 2020. (https://www.dgrm.mm.gov.pt/web/guest/as-pem-diretiva-quadro-estrategia-marinha)
MM, SRMCT, SRAAC (2020). Estratégia Marinha: relatório do 2º ciclo. Ministério do Mar Secretaria Regional do Mar, Ciência e Tecnologia, Açores, e Secretaria Regional de Ambiente, Recursos Naturais e Alterações Climáticas, Madeira. Março de 2020. (https://www.dgrm.mm.gov.pt/web/guest/as-pem-diretiva-quadro-estrategia-marinha)
MM, SRMCT, SRAAC (2020). Estratégia Marinha: relatório do 2º ciclo. Ministério do Mar Secretaria Regional do Mar, Ciência e Tecnologia, Açores, e Secretaria Regional de Ambiente, Recursos Naturais e Alterações Climáticas, Madeira. Março de 2020. (https://www.dgrm.mm.gov.pt/web/guest/as-pem-diretiva-quadro-estrategia-marinha)
MM, SRMCT, SRAAC (2020). Estratégia Marinha: relatório do 2º ciclo. Ministério do Mar Secretaria Regional do Mar, Ciência e Tecnologia, Açores, e Secretaria Regional de Ambiente, Recursos Naturais e Alterações Climáticas, Madeira. Março de 2020. (https://www.dgrm.mm.gov.pt/web/guest/as-pem-diretiva-quadro-estrategia-marinha)