Trends in Marine Alien Species (MAS)
Justification for indicator selection
Biological invasions are widely perceived as one of the main threats to biological diversity next to habitat destruction. Of particular importance are the Invasive species namely those introduced alien species that establish themselves, spread rapidly and can threaten biological diversity in various ways, from reducing genetic variation and eroding gene pools, through the extinction of endemic species, and by altering habitat and ecosystem functioning (Hulme, 2007).
Invasive alien species have not been taken into enough consideration concerning the European Water Framework Directive (WFD) the Marine Strategy Framework Directive (MSFD) and other European directives until recently (Cardoso & Free, 2008; Olenin et al, 2007).
A factor determining good ecological quality and functioning of the ecosystem is high biodiversity. Intruding alien species can greatly influence these factors. A species such as the colonial seasquirt Didemnum vexillum could put great stress on the biodiversity in an area by covering many square kilometres of sea floor and overgrowing other indigenous species. Alien species can also hamper functions of water bodies that are important for humans, including shipping, fisheries, aquaculture production, recreation, public health, tourism
The ecological impacts of invasions are often inferred from distribution data under the assumption that the more abundant the alien species, the more severe the impact (Vila et al, 2010). There have been more than 1300 marine species introduced in European Seas (Katsanevakis et al., 2013) and the impact of them on local ecosystems has been studied for less than 100 of them.
In the lack of data on impacts (as well as trends) of most of the introduced species in European Seas, the trends in NIS – Non Indigenous species (all introduced species) is used as a proxy of the trends of the most invasive marine alien species.
- Hulme PE. 2007. Biological invasions in Europe: drivers, pressures, states, impacts and responses. In: Hester R and Harrison RM (Eds). Biodiversity under threat. Cambridge, UK: Cambridge University Press.
- Leppakoski, E., and S. Olenin. 2000. Non-native species and rates of spread: lessons from the brackish Baltic Sea. Biological Invasions 2:151–163.
- Raitsos D., Beaugrand G., Georgopoulos D. Zenetos A; Pancucci-Papadopoulou M. A, Theocharis A., & Papathanassiou E., 2010. Global climate change amplifies the entry of tropical species into the Eastern Mediterranean Sea. Limnology & Oceanography, 55(4), 1478–1484
- Streftaris, N, Zenetos, A. and E. Papathanassiou, 2005. Globalisation in marine ecosystems - The story of non indigenous marine species across European Oceanography and Marine Biology: An Annual review. 43: 421-455
- Wonham, M.J., Carlton, J.T., 2005. Trends in marine biological invasions at local and regional scales: the Northeast Pacific Ocean as a model system. Biological Invasions 7, 369–392.
- Meyerson, L.A. & Mooney, H.A. (2007) Invasive alien species in an era of globalization. Frontiers in Ecology and the Environment, 5, 199–208.
- Vila M, Basnou C, Pysek P, Josefsson M, Genovesi P et al., 2010. How well do we understand the impacts of alien species on ecosystem services? Front. Ecol. Environ. 8: 135–144.
- Olenin S, Minchin D, Daunys D, 2007. Assessment of biopollution in aquatic ecosystems. Marine Pollution Bulletin 55: 379–394.
- Cardoso AC & Free G, 2008. Incorporating invasive alien species into ecological assessment in the context of the Water Framework Directive. Aquatic Invasions 3: 361–366.
- Katsanevakis, S., Gatto, F., Zenetos, A., & Cardoso, A. C. (2013). How many marine aliens in Europe? Management of Biological Invasions, 4(1), 37-42.
The indicator for the marine and estuarine species represents the cumulative number (i.e. the sum) of primary producers (plants), invertebrate and vertebrate alien species that have been recorded in European waters since 1950
Number of species per group (primary producers, invertebrate and vertebrates) at Pan-European level, at regional level (MSFD area) and at country level (only countries with marine borders).
Policy context and targets
Increase in trade, tourism and maritime, as well as the development in aquaculture, and fisheries, have provided new and enhanced pathways for the spread of alien invasive species. Although European states have a comprehensive regulatory framework to protect economic interests against diseases and pests, these are often inadequate to safeguard against species that threaten native biodiversity. Moreover, the regulatory system pertains to pathogens while large sized species that may have considerable impact on health, economy are not considered to date.
The Convention on Biological Diversity (CBD) has recognized an urgent need to address the impact of Invasive Alien Species and has included ´Trends in invasive alien species’ in the trial indicators to be developed and used for assessing global progress towards the 2010 target.
In Europe, trends in invasive alien species is one of the SEBI2010 WG5 indicators http://biodiversity-chm.eea.eu.int/information/indicator/F1090245995, which has been materialised for the marine environment by exhibiting trends in MAS (Marine alien species).
Both MSFD and WFD have recently included «Non Indigenous species» among indicators required for assessing /setting the overall objective which is Good Environmental Status (to be restored or maintained by 2020) and Good Ecological Status (to be reached by 2015) respectively. Trends in MAS related to shipping, aquaculture, trade will be a tool towards this particularly in hot spot areas such as ports, lagoons, aquaculture areas. A levelling- off the current increase in cumulative numbers of alien species and a reduction in the rate of establishment of alien species in new countries/regions by MAS and/or a shrinking distribution of these within European Seas would be a signal that this target is addressed successfully.
Related policy documents
Animal health legislation
COM(2008) 789 Final
Communication from the Commission to the Council, the European Parliament, the European Economic and Social Committee and the Committee of the Regions Towards an EU Strategy on Invasive Species [SEC(2008) 2887 Et SEC(2008) 2886
Council Directive 90/220/EEC of 23 April 1990
Council Directive 90/220/EEC of 23 April 1990 on the deliberate release into the environment of genetically modified organisms
Council Regulation (EC) No 708/2007 of 11 June 2007
Council Regulation (EC) No 708/2007 of 11 June 2007 concerning use of alien and locally absent species in aquaculture. Applying to any non-routine intentional introduction of alien or locally absent aquaculture species. Publicly available register on all introductions and translocations of alien or locally absent aquaculture species (applications, permits, monitoring). Monitoring for all alien or locally absent aquaculture species after their release (2 years or full generation cycle or longer). Contingency plans for non-routine introductions or pilot releases of alien or locally absent aquaculture species, to be implemented in case of negative effects on the environment or on native populations
European Commission (2006). Proposal for a Council Regulation concerning use of alien and locally absent species in aquaculture.
COM(2006) 154 final: 32 pp.
Marine Strategy Framework Directive 2008/56/EC
Directive 2008/56/EC of the European Parliament and of the Council of 17 June 2008 establishing a framework for community action in the field of marine environmental policy (Marine Strategy Framework Directive)
Water Framework Directive (WFD) 2000/60/EC
Water Framework Directive (WFD) 2000/60/EC: Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy.
Key policy question
Are marine invasive aliens increasing in European Seas?
Specific policy question
Is the number of alien species in European Regional Seas (MSFD areas) increasing or decreasing?
Methodology for indicator calculation
A simple information system herein called HCMR/EEA database has been developed in HCMR since 2002 to serve as a resource in developing a trends indicator and for reporting to EEA. The Mediterranean component of it has been transferred to EASIN. Data is available for all European countries both at country level and at MSFD level (Baltic Sea, North Sea, Icelandic Sea, Celtic, Iberian Shelf+ Biscay, 4 Mediterranean, Black Sea). Details are currently archived for 2487 aquatic species, and 7795 records at both country and MSFD level. Harmonisation of the HCMR/EEA database with European marine alien species databases was an EEA exercise in 2009 towards updating the marine alien species trends indicator the SEBI2010.
For countries with borders in more than one MSFD area, the species belonging to each area have been sorted out after consultation with experts such as in UK, Denmark; and/or by investigating the national databases such as in Sweden, Norway; and/or based on scientific reviews such as for Germany; or in the case of Mediterranean countries from the Marine Mediterranean Invasive Alien Species database which encompasses the MSFD area distribution.
The list of national experts contacted is presented below.
The year of first collection date (or first report when the former is missing) has been compiled for each MSFD area separately. For the Pan European analysis, the very first collection/reporting date is considered.
Number of new introduced marine (including brackish waters) alien species is presented per decade since 1950 at Pan European level and per MSFD area.
Information is broken down per selected taxonomic groups: vertebrates, invertebrates and plants (chromista, vascular plants, algae and fungi). The vast majority of animals exempting fish and Mammalia are classified as Invertebrates. Birds have been excluded from calculations.
Established, non established and cryptogenic species are considered. Very old records reported as «extinct» in the literature and species suspected to be present due to natural expansion from one MSFD area to the neighbouring one, are excluded from calculations.
In the graphs that follow, each of the MSFD is treated separately, i.e., introduced species in more than one MSFD have been recorded in each of them. Care has been taken to ensure that the nomenclature problems encountered (e.g., the same species recorded in different regions, lists, or data banks with different names, i.e., synonyms) have not resulted in multiple separate recordings. Scientific literature published lately (2009-2013) has sorted out taxonomic problems and revised nomenclature in some cases (i.e. Marenzelleria, Mnemiopsis). Thus, some species, which are reported as aliens in national databases, have been excluded as native ones. Synonyms of species reported differently in existing European systems have been sorted out by using the nomenclature of WoRMS (World Registry of Marine Species) WoRMS Editorial Board (2013). World Register of Marine Species. Available from http://www.marinespecies.org at VLIZ.
In an case, the HCMR/EEA database is continually updated based on:
a) latest updates of European online databases such as DAISIE, NOBANIS, ESENIAS, AquaNIS,
b) annual reports of the ICES Working Group on Introduction and transfers of Marine Organisms and ICES/IOC/IMO Working Group on Ballast and Other Ship Vectors. The group meets annually and function through extensive collaboration by expert scientists from all over the world, representing leading knowledge and expertise on this topic. They keep annual records on new invasions in the ICES area and provide management advice upon request
c) results of research projects such as PERSEUS, COCONET, VECTORS
d) scientific publications –see list of latest publications per MSFD area
e) personal communication with renown scientist
Methodology for gap filling
Personal communication with national experts and taxonomic experts - see list of contacted experts below.
When exact data of alien reporting is not known the year of the relative publication has been used.
The following individual local experts were contacted:
Belgium: Sonia VANDERHOVER, Etienne BRANQUART, Francis KERKOFF
Denmark: Kathe Rose JENSEN, Mads THOMSEN
Estonia: Henn OLJAVEER, Andres JAANUS
Finland: Maiju LEHNAMEN, Reetta LJUNGBERG
France: Marc VERLAQUE, Philippe GOULLETQUER, Laurence MIOSSEC
Germany: Ralf BANSTROP, Stephan GOLLASCH, Stefan NEHRING
Italy: Adriana ZINGONE, Carla MORRI
Lithuania: Anastasia ZAIKO
Malta: Patric SCHEMBRI
Netherlands: Rob LEWIS, Hans De BAUWE, Marco FAASE, Herre STEGENGA, 'Arjan GITTENBERGER
Norway: Vivian HUSA
Poland: Michal GRABOWSKI, Mykola OVCHARENKO
Portugal: Anna AMORIM
Russia: A. BEREZINA
Spain: Javier CREMADES UGARTE
Turkey: Melih CINAR
UK: John S RYLAND, Liz COOK
- ICES. 2007. Status of introductions of non-indigenous marine species to the North Atlantic and adjacent waters 1992–2002. ICES Cooperative Research Report No. 284. 149 pp.
- ALIENS: Algal introductions to european shores
- ISSG: Global Invasive Species Database
- BSASP : Baltic Sea Alien Species databases Last update 25.10.10. The Baltic Sea Alien Species Database became a part of the Integrated Information system AquaNIS.: http://www.corpi.ku.lt/databases/index.php/aquanis/
- ICES WGITMO 2002-2013 reports
- ALARM: Assessing Large scale Risks for Biodiversity with Tested Methods
- IMPASSE: Environmental Impacts of Alien Species in Aquaculture
- INSPECT – Marine alien species introduced into Portuguese estuaries and coastal areas: patterns of distribution and abundance, vectors and potential of invasion (2009-2011) A paper was published after this project: Costa & Chainho (2011). Costa MJ & Chainho P (2011) Projeto INSPECT - Espécies exóticas marinhas introduzidas em estuários e zonas costeiras Portugueses. Ecologi@ 3: 73-74.
- VECTORS: AquaNIS
EEA data references
- No datasets have been specified here.
External data references
- Information system on Aquatic Non-Indigenous species (dataset URL is not directly available)
- BSASD - Baltic Sea Alien Species Database (dataset URL is not directly available)
- ELNAIS - invasive alien species data (dataset URL is not available)
- HCMR DataBase
- ICES/IMO/IOC WGITMO report 2002-2012-2013
- EASIN - European Alien Species Information Network (Dataset URL is not available)
- NOBANIS - European Network on Invasive Alien Species
- MAMIAS - Marine Mediterranean Invasive Alien Species (Dataset URL is not available)
- Regional Euro-Asian Biological Invasions Centre (dataset URL is not available)
- ICES/IMO/IOC WGBOSV report 2002-2012-2013
- EPPO lists and documentation on invasive alien plants (dataset URL is not available)
Data sources in latest figures
Year of introduction is based on reported first collection dates but do not necessarily imply true year of introduction that may be years earlier.
For the last 3 years (2011-13) rate of introduction is an underestimate. Species collected in the 2011-13 period are expected to be published in the next 5 years.
In the lack of data on impacts (as well as trends) of most of the introduced species in European Seas, the trends in NIS - marine alien species (all introduced species) is used as a proxy of the trends of the most invasive marine alien species.
Data sets uncertainty
Data sets even for the Baltic, which is one of the most studied Seas, are often contradicting among official sources such as NOBANIS, HELCOM and the Baltic Seas Alien Species database. The same holds true for the North Sea whose south eastern borders (Kattegat) are overlapping with the Baltic Sea ones. Individual experts were contacted in many cases.
In the Black Sea it appears that many copepod species were added to the Ukrainian aliens list based on unsubstantial records. Some have been eliminated from the previous list (A. Cubanova pers. commun.). Yet, the number of marine invertebrates (mostly copepods) is rather inflated and needs further revision.
Cryptogenic species are included by most scientists, excluded by others as native. In many cases historical introductions such as the ship worm Teredo navalis are not perceived as aliens and not included in lists. Species reported from drift material washed ashore are included as casual records.
The list for Mediterranean alien species is still an underestimate as it does not include monocellular algae. Bearing in mind that the diversity of marine microalgae is scarcely known in wide areas of the Mediterranean Sea it can rarely be excluded that a suspected microalgal invader was already present as part of the rare, hidden and un-sampled phytoplankton, we refrain from citing a detailed list of plankton.
The picture reflects somehow the scientific effort not only in discovering/reporting new species or mapping their distribution but even compiling data at national level.
Climate change is proved to enhance establishment of alien species (see Raitsos et al, 2010). Consequently, it skews the real magnitude of the phenomenon.
Short term work
Work specified here requires to be completed within 1 year from now.
Work descriptionUpdate lists and collection dates provided by ongoing research and monitoring projects at national level. Analyse the most invasive species as concluded from their spread versus their origin and mode of introduction and impact on ecosystem services.
Deadline2013/01/01 01:00:00 GMT+1
Work descriptionUpdate the distribution lists based on data to be collected/reported in the course of future monitoring projects at national level/ compiled lists/databases at national level. Considering the difficulties of reporting new alien species and monitoring the invasive ones, engage citizens and NGOs into reporting selected target species through national/international networks such as the jellyfish watch, eye on earth etc. Expand the existing system by incorporating info on impacts of as many IAS as possible.
Deadline2016/01/01 01:00:00 GMT+1
Long term work
Work specified here will require more than 1 year (from now) to be completed.
Responsibility and ownership
EEA Contact InfoTrine Christiansen
For references, please go to http://www.eea.europa.eu/data-and-maps/indicators/trends-in-marine-alien-species-mas or scan the QR code.
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