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PERSPECTIVE article

Front. Appl. Math. Stat., 30 June 2017
Sec. Environmental Informatics and Remote Sensing
This article is part of the Research Topic Data Mining and Methods for Early Detection, Horizon Scanning, Modelling, and Risk Assessment of Invasive Species View all 11 articles

Seven Recommendations to Make Your Invasive Alien Species Data More Useful

  • 1Botanic Garden Meise, Bouchout Domain, Meise, Belgium
  • 2Research Institute for Nature and Forest, Brussels, Belgium
  • 3U.S. Geological Survey, Core Science Analytics, Synthesis, and Libraries Program, Reston, VA, United States
  • 4Aquatic and Terrestrial Ecology, Operational Directorate Natural Environment, Royal Belgian Institute of Natural Sciences, Brussels, Belgium
  • 5Department of Ecology and Systematics, Faculty of Biology, National and Kapodistrian University of Athens, Panepistimiopolis, Greece
  • 6EASIN, European Commission Joint Research Centre, European Commission, Joint Research Centre, Ispra, Italy
  • 7CABI, Nosworthy Way, Wallingford, Oxfordshire, United Kingdom
  • 8Department of Forest Biodiversity, University of Agriculture in Krakow, Krakow, Poland
  • 9Finnish Environment Institute, Helsinki, Finland
  • 10Global Biodiversity Information Facility, Copenhagen, Denmark
  • 11Swedish Environmental Protection Agency, Stockholm, Sweden
  • 12CERIS, Institute of Technology, Sligo, Ireland
  • 13Institute for Plant Protection and Environment, Belgrade, Serbia
  • 14Forest Research Institute, Raszyn, Poland
  • 15Department of Invasion Ecology, Institute of Botany, The Czech Academy of Sciences, Průhonice, Czechia
  • 16Faculty of Agriculture, University of Belgrade, Belgrade, Serbia
  • 17SPW-DEMNA, Département de l'Étude du Milieu Naturel et Agricole, Gembloux, Belgium
  • 18Department of Geosciences and Natural Resource Management, Faculty of Science, University of Copenhagen, Frederiksberg, Denmark
  • 19INRA, UR633, Zoologie Forestière, Orléans, France
  • 20Centre for Ecology and Hydrology, Wallingford, United Kingdom
  • 21IUCN SSC Invasive Species Specialist Group, Rome, Italy
  • 22Università degli Studi di Firenze, Firenze, Italy
  • 23Institute of Biodiversity and Ecosystem Research, Bulgarian Academy of Sciences, Sofia, Bulgaria
  • 24Natuurpunt, Mechelen, Belgium
  • 25Institute of Marine Biological Resources and Inland Waters, HCMR, Anavyssos, Greece
  • 26Belgian Biodiversity Platform, Walloon Research Department for Nature and Agricultural Areas, Service Public de Wallonie, Gembloux, Belgium

Science-based strategies to tackle biological invasions depend on recent, accurate, well-documented, standardized and openly accessible information on alien species. Currently and historically, biodiversity data are scattered in numerous disconnected data silos that lack interoperability. The situation is no different for alien species data, and this obstructs efficient retrieval, combination, and use of these kinds of information for research and policy-making. Standardization and interoperability are particularly important as many alien species related research and policy activities require pooling data. We describe seven ways that data on alien species can be made more accessible and useful, based on the results of a European Cooperation in Science and Technology (COST) workshop: (1) Create data management plans; (2) Increase interoperability of information sources; (3) Document data through metadata; (4) Format data using existing standards; (5) Adopt controlled vocabularies; (6) Increase data availability; and (7) Ensure long-term data preservation. We identify four properties specific and integral to alien species data (species status, introduction pathway, degree of establishment, and impact mechanism) that are either missing from existing data standards or lack a recommended controlled vocabulary. Improved access to accurate, real-time and historical data will repay the long-term investment in data management infrastructure, by providing more accurate, timely and realistic assessments and analyses. If we improve core biodiversity data standards by developing their relevance to alien species, it will allow the automation of common activities regarding data processing in support of environmental policy. Furthermore, we call for considerable effort to maintain, update, standardize, archive, and aggregate datasets, to ensure proper valorization of alien species data and information before they become obsolete or lost.

1. Introduction

Sound decision-making to minimize the risk associated with the introduction of alien species requires accurate and up-to-date data and the knowledge derived from them. These data feed into a wide range of processes to tackle problematic invasive alien species and are needed to develop an appropriate, evidence-based response (Table 1). Horizon scanning (the systematic examination of future potential threats and opportunities, leading to their prioritization), risk assessment, risk management, early detection and rapid response all depend on accurate and accessible data [14]. So, although alien species data are little different from data on other species, the demands we place on these data are considerable and specific.

TABLE 1
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Table 1. Data/information categories and their invasive alien species-related evidence-based processes.

Current invasive alien species policies depend on the availability and quality of data. For example, the EU regulation no. 1143/2014 on Invasive Alien Species [5], requires member states to report on the status of invasive alien species of Union concern and their progress in managing them, likewise similar regulations exist in other countries, such as the USA [6]. Responsible authorities need access to timely and validated data and they need to report this in a standardized way, so it can be collated nationally and internationally. Within the EU, the European Alien Species Information Network (EASIN) [7, 8] has been developed to this end, including a mechanism for quality assurance, safeguarding and improvement [9].

Mitigating and preventing biological invasions present particular challenges with regard to the quality, relevance and scope of data sources and infrastructure [10]. The numerous origins of the data and broad taxonomic scope, combined with the global geographic extent and input from diverse disciplines make proper handling of alien species data difficult, but also necessary. With this perspective, we gathered database managers, data users, data generators and biodiversity informatics specialists to outline how alien species data can be made more useful, taking into account the peculiarities and applications of such data. This resulted in seven recommendations, which, if followed, would improve the use of alien species data for research, policy and management purposes. Some of these recommendations are not unique to alien species data, but their impact would be particularly significant in this discipline.

2. Approach

Correspondence A workshop titled Data for invasive species research, policy making and management was organized in Brussels in 2016 with representatives from sixteen European countries and the United States. The attendees were from the European Alien Challenge COST1 Action, from important institutions and projects related to alien species data such as the European Alien Species Information Network (EASIN), Delivering Alien Invasive Species Inventories for Europe (DAISIE), Global Biodiversity Information Facility (GBIF), Global Invasive Species Information Network (GISIN), Centre for Agriculture and Biosciences International Invasive Species Compendium (CABI–ISC), and the Biodiversity Information Standards organization (formerly known as the Taxonomic Databases Working Group and referred to by the acronym TDWG). Effort was made to balance participant representation in terms of gender, country of origin within Europe and taxonomic and habitat interests (terrestrial, freshwater and marine).

The workshop consisted of talks and participatory exercises on four main invasive alien species themes: risk assessment, horizon scanning, management and monitoring. For each of these themes, participants reflected on the data needs and requirements (Table 1), the data sources they commonly use, and the existing data standards. Materials from the workshop have been deposited in an open repository [11]. Conclusions reported by breakout groups were refined and supplemented in facilitated plenary discussion. Particular attention was paid to the perspectives of both the data publishers and data users.

During the workshop a number of opportunities for facilitating proper use and valorization of alien species data was identified and these resulted in the recommendations presented below and summarized in Table 2.

TABLE 2
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Table 2. Seven recommendations for improving the usefulness of alien species data.

3. Create Data Management Plans

A DMP describes how the information generated by a project will be handled both during and after it is generated. These plans define responsibilities; aim to avoid data loss and incompatibility by indicating how data will be preserved and formatted; stipulate what metadata are required to understand the data; and consider data sharing options, including licensing [12].

Such plans are a means to improve data management and are now commonly required by funding agencies. The US National Science Foundation has required them since 2010 [13] and in 2013 the European Commission launched a pilot on open research data requiring a DMP in the first 6 months of the project [14]. The DMP approach also encourages journals to change their policies toward the archiving of data, though it is taking time for the whole scientific community to embrace these changes [15, 16]. Typical minimum sections of a DMP are: (i) What type of data and metadata are expected? (ii) Which standards are used for alien species data? (iii) How should data be shared? (iv) How should data be permanently preserved? Researchers new to writing a DMP should refer to their institutional and funding agency guidelines if any, and, with respect to invasive species data, recommendations for ecologists [6, 17].

Strictly speaking, each recommended action could be implemented without the need to compile a DMP. However, preparing and agreeing upon a DMP ensures a holistic approach to data management and increases its openness and accountability, while also answering the needs from funding agencies and institutional data policies [12], so we recommend their use.

4. Document Through Metadata

Good metadata provide information on provenance, scope, methods, limitations, data formats and units to facilitate correct data use, as well as license and contact information. USGS' Data Management Web site2 lists multiple tools and best practices for metadata creation. Several metadata standards for biodiversity data are available: such as Ecological Markup Language (EML 18) adopted by GBIF [19]; the INSPIRE directive framework (Infrastructure for Spatial Information in Europe)3, which describes geospatial data and the Data Catalog Vocabulary (DCAT)4, to describe datasets. We have not identified any specific metadata standards for alien species data and recommend the use of the metadata standards above, for which tools and services are already available [20]. An example of a tool for metadata standardization is the desktop application Morpho5, which guides users through the creation of EML [21]. Morpho can interface with a MetaCat registry to provide a searchable catalog of ecological datasets. This technology is used by both the DataONE repository6 and the European Biological Observations Network (EU BON) [22]. Creating metadata may seem secondary to primary data curation, but metadata are essential to ensure the data can be discovered and used in the long term [23]. In the context of alien species data, improved access to metadata could enhance the speed with which data are found and mobilized.

5. Improved Interoperability of Information Sources

Information on alien species is scattered among a multitude of sources, including databases; peer-reviewed and gray literature; unpublished research projects and institutional datasets [8, 24]. Important international sources of these data include the 2000 Global Invasive Species Database (GISD) of the IUCN/SSC Invasive Species Specialist Group (ISSG) [25]; the 2004 Global Invasive Species Information Network (GISIN); and the Global Invasive Alien Species Information Partnership (GIASIP), as well as global information providers such as the CABI Invasive Species Compendium (ISC) and the Global Register of Introduced and Invasive Species (GRIIS). Any new initiative to collate data needs to consider its role and define its niche within a complex environment of global, continental, national and regional data repositories [7, 26].

Almost any effort to compile and harmonize data from these sources is impeded by differences in field names, definitions, and taxonomy, as well as access and license restrictions [3, 27]. The use of common standards for all these aspects can improve the interoperability of these data sources: their data can be more efficiently exchanged, combined, compared, and presented. In addition, data processing should ideally be performed in a repeatable way, to increase the efficiency of activities such as horizon scanning and risk assessment. For invasion policies to be proactive, these activities should be repeated at regular intervals [2].

Online alien species catalogs and invasive alien species information systems are difficult to keep up-to-date [28, 29], yet they provide a wide variety of valuable information. Funding for these initiatives has been sporadic at best [28] and is often time-limited [29]. Thus relevant information stored and managed within such initiatives become quickly out-dated, and efforts to keep them updated are often suddenly discontinued. This tends to spread errors to other systems that are populated with data from such sources, particularly if provenance is poorly tracked. As such, the current process restricts alien species data exchange, aggregation, interoperability and even rescue. Technological advances have boosted the number of initiatives [30], but also increased the data's volume and complexity [23, 3133]. A holistic approach to complex biological questions requires more from data than a traditional reductionist approach, as demonstrated by the success of the Gene Ontology [34]. Yet this poses additional challenges of ensuring data quality, data curation, interoperability and future-proofing against obsolete technology and increasing data volumes [35]. Technological change promises many improvements in data collection, with systems such as smartphones equipped with built-in GPS, image capture, external sensors, and automated and expert validation [31]. Also, advances in species detection through environmental DNA, such as those of Dejean et al. [32], need support to be included within alien species initiatives.

We recommend that alien species databases work together to follow common standards and that these standards are further developed for emerging data streams.

6. Format Data Using Existing Standards

Within the scope of a single dataset, data only need to be formatted consistently to be usable. However, to combine datasets for broad-scale analysis, a community-defined exchange format or standard is required to allow data interoperability. Among the qualities of a “good standard” are that it be readable (by both humans and machines), simple, learnable and efficient [36].

The alien species research community is not universally aware of biodiversity informatics standards, where they come from and how they can be extended. Standards for the exchange of biodiversity data, including alien species data, are developed, discussed and promoted by the Biodiversity Information Standards organization, TDWG [37]. This organization is the guardian of Darwin Core, the most widely adopted standard to exchange biodiversity information related to species [38]. By following these standards, data managers can avoid duplication of effort and mistakes. Furthermore, the organization can give advice and support for updating existing standards and proposing new ones. It is recommended that the invasive alien species community continue to engage in TDWG, both to adopt standards for common terms and to establish standards specific to invasion biology.

7. Adopt Controlled Vocabularies for Four Alien Species Properties

In addition to a standard format to exchange data, specialist communities often also require further control on the values of terms to increase interoperability. This can be achieved by adopting controlled vocabularies. This not only means that data can be merged, but also contributes to the normative definition of a term.

Four alien species properties were identified that are either missing from Darwin Core or lacking a reference to a recommended controlled vocabulary. These are introduction pathway, degree of establishment, impact mechanism, and species status. For each of these, vocabularies exist outside Darwin Core, yet these currently exist as frameworks and require further work to be developed into standards.

For pathway terminology, the need for a consistent classification, hierarchy, and terminology has long been recognized [3941]. Meanwhile, a standardized hierarchical pathway classification was adopted by parties to the Convention of Biological Diversity [42] and is being applied to existing databases [9, 43].

A framework for the degree of establishment has been presented by Blackburn et al. [44]. This hierarchical classification provides a terminology for populations at different points in the invasion process (casual/introduced, alien, naturalized/established, invasive) and allows expression of the range of establishments from those organisms only kept in cultivation or captivity through to full naturalization and invasiveness.

For alien species impact, a classification of categories based on the magnitude of environmental impacts was developed by Blackburn et al. [45], and has been adopted by the IUCN in 2016. However, for impacts other than environmental, such as socio-economic, plant health, human health and animal health, no comprehensive overview is available, but several protocols have been developed for risk assessment that can provide inspiration for classifications (see [46] for an overview).

Standards from the trade and agriculture sectors can be useful in describing species status, for example, the International Plant Protection Conventions International Standard for Phytosanitary Measures: specifically, IPSM 87, Determining pest status in an area; and IPSM 68, Guidelines for surveillance. We recommend these controlled vocabularies are expressed in a machine-readable format and are referenced from the appropriate terms in Darwin Core. This is in line with the recommendations of the GBIF Task Group on Data Fitness for use in Research into Invasive Alien Species [33].

Additionally, controlled vocabularies might prove helpful in the dissemination of information on species management [47]. Good examples are the Global Eradication and Response Database [48] and the Database of Island Invasive Species Eradications [49]. The documentation of management actions in the field and the storage of these data are key to performing cost-benefit analyses of management measures.

8. Increase Data Availability

Much has already been written about the methods and needs for open data publication [3, 17, 50]. Beyond the good intentions, Invasivesnet is a developing global association for open knowledge and open data on alien species [51]. This association will facilitate greater understanding, communication, and improved management of biological invasions globally, by developing a sustainable network of networks for effective knowledge exchange. The association fosters tool development and cyberinfrastructure for the collection, management and dissemination of data and information on alien species from a range of sources (e.g., research, citizen science). The key point is that data should be shared and standardized to ensure interoperability [52]. In the case of species observation data a straightforward solution is to publish through a repository such as GBIF or the Ocean Biogeographic Information System (OBIS), as it ensures adherence to a minimum of common standards.

There can be little doubt that data sharing using community standards and adequate metadata are of benefit to research and society in general [53]. Yet motivating good data management is not easy when practitioners are not rewarded by their institutions. However, this is changing [54, 55], particular with the support of aspirational statements such as the Berlin9 and Bouchout10 declarations, which show the willingness of some institutions and individuals to change. Also, there are now policy initiatives in place, such as the EU INSPIRE directive11 or the United States Administration's Open Data Policy12,13, to mandate harmonization of spatial data.

9. Ensure Long-Term Data Preservation

Under ideal circumstances databases would have funding for maintenance and updating for as long as they are useful, however, this is unrealistic. Furthermore, the end of a project is the wrong time to consider the long-term persistence of data [29, 56]. Data actively being curated are often best maintained close to their source, however, longevity can be built-in to procedures by periodically depositing data in an open repository, not just on a personal or university website. Hence, data are protected from catastrophic events, human attrition, and the slow degradation of obsolescent hardware, which is the fate of much data [57]. If a publication is based upon a specific dataset it is good practice to deposit that precise version in a repository.

Not all repositories are the same, for example the Dryad14 and Zenodo15 repositories are general-purpose repositories able to accept data in ad hoc formats, not necessarily formatted to community standards. They provide flexibility, however, repositories dedicated to one data type provide much greater opportunities for integration due to their enforcement of standards. Examples of such repositories are GBIF and GenBank [58]. Repositories also differ in their ability to embargo the release of data and in the licensing options. We recommend that considerable a priori thought goes into data preservation and the choice of repository.

10. Conclusion

Many alien species databases have emerged either before or without knowledge of existing standards for database management in biodiversity informatics. Furthermore, existing standards do not adequately cover all the needs of the research domain. Not all ecologists have strong information technology skills, nor are experts in technology-mediated collaboration, shared instrumentation or standardized data collection [59]. In the rapidly changing information technology landscape, ecologists and conservationists cannot be expected to keep up with developments in software and data standards. This should encourage data managers, wherever possible, to simplify the tools created for ecological practitioners. This becomes more pressing as new technologies are used to provide data on alien species.

Many data management issues are common to all biodiversity data, yet species native range, introduction pathway, degree of establishment and impact mechanism are specific to alien species. Additionally, the need for fast dissemination of information and data is typical to alien species, in particular early detection and rapid response programs. Proactive responses to biological invasions require repeatable workflows for horizon scanning and risk assessment [60]. Adoption of standards and controlled vocabularies for this information can boost the usefulness for alien species research, policy-making and policy evaluation. There is a need for the acceptance of common data standards that take into consideration the needs of both data collectors and diverse data users, from the science community to the end user.

Work is required with the research and education communities and the standards authorities to ensure that suggested standards are shepherded through acceptance and implementation and that these standards are introduced early within the education of young scientists and promoted among those in the biodiversity community, so that they are adopted widely. Improving core biodiversity standards for their content and usefulness for alien species data will allow the automation of common activities needed to tackle biological invasions. We call for considerable effort toward maintaining, updating, standardizing, and archiving or incorporating current data sets, to ensure proper valorization of alien species data and resulting information before they become obsolete or lost.

Author Contributions

QG, ACC, JP, SV, and TA wrote the original briefing note, which outlined the idea of a workshop on biodiversity data interoperability for invasive species. SV, QG, TA, PD, AD were the local organizers of the Workshop and prepared the initial draft of the paper. HR is Chair of the COST Action and has supported and attended the workshop. AS participated in the workshop, contributed to the writing of the paper, and arranged for the initial peer review of the manuscript through the U.S. Geological Survey. All other authors contributed to the writing of the paper and attended the workshop.

Funding

This article is based upon work from COST Action TD1209 ALIEN Challenge, supported by COST (European Cooperation in Science and Technology) www.cost.eu. JP was partly supported by the long-term research development project no. RVO 67985939.

Conflict of Interest Statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Acknowledgments

We also thank the Belgian Biodiversity Platform, funded by the Belgian Science Policy Office, for the use of their facilities, and the U.S. Geological Survey, for previous peer review. Any use of trade, product, or firm names in this article is for descriptive purposes only and does not imply endorsement by the U.S. Government.

Footnotes

References

1. McGeoch MA, Spear D, Kleynhans EJ, Marais E. Uncertainty in invasive alien species listing. Ecol Appl. (2012) 22:959–71. doi: 10.1890/11-1252.1

PubMed Abstract | CrossRef Full Text | Google Scholar

2. Roy HE, Peyton J, Aldridge DC, Bantock T, Blackburn TM, Britton R, et al. Horizon scanning for invasive alien species with the potential to threaten biodiversity in Great Britain. Global Change Biol. (2014) 20:3859–71. doi: 10.1111/gcb.12603

CrossRef Full Text | Google Scholar

3. Groom QJ, Desmet P, Vanderhoeven S, Adriaens T. The importance of open data for invasive alien species research, policy and management. Manage Biol Invasions (2015) 6:119–25. doi: 10.3391/mbi.2015.6.2.02

CrossRef Full Text | Google Scholar

4. Zenetos A, Çinar ME, Crocetta F, Golani D, Rosso A, Servello G, et al. Uncertainties and validation of alien species catalogues: the Mediterranean as an example. Estuarine Coast Shelf Sci. (2017) 191:171–87. doi: 10.1016/j.ecss.2017.03.031

CrossRef Full Text | Google Scholar

5. European Union. Regulation (EU) No. 1143/2014 of the European Parliament and of the Council on the prevention and management of the introduction and spread of invasive alien species. Official J Eur Union (2014) 317:35–55.

6. Executive Office of the President. Safeguarding the nation from the impacts of invasive species. Federal Register (2016) 81:88609–14.

7. Katsanevakis S, Bogucarskis K, Gatto F, Vandekerkhove J, Deriu I, Cardoso AC, et al. Building the European Alien Species Information Network (EASIN): a novel approach for the exploration of distributed alien species data. Bioinvasions Records (2012) 1:235–45. doi: 10.3391/bir.2012.1.4.01

CrossRef Full Text | Google Scholar

8. Katsanevakis S, Deriu I, D'Amico F, Nunes AL, Pelaez Sanchez S, Crocetta F, et al. European alien species information network (EASIN): supporting European policies and scientific research. Manage Biol Invasions (2015) 6:147–57. doi: 10.3391/mbi.2015.6.2.05

CrossRef Full Text | Google Scholar

9. Tsiamis K, Cardoso AC, Gervasini E. The European Alien Species Information Network on the Convention on Biological Diversity pathways categorization. NeoBiota (2017) 2:21–29. doi: 10.3897/neobiota.32.9429

CrossRef Full Text | Google Scholar

10. Latombe G, Pyšek P, Jeschke JM, Blackburn TM, Bacher S, Capinha C, et al. A vision for global monitoring of biological invasions. Biol Conserv. (2016). doi: 10.1016/j.biocon.2016.06.013. [Epub ahead of print].

CrossRef Full Text | Google Scholar

11. Groom Q, Adriaens T, Desmet P, Wever AD, Vanderhoeven S. Resources from the Workshop “Data for Invasive Species Research, Policy Making and Management”. doi: 10.5281/zenodo.261743

CrossRef Full Text

12. McLure M, Level AV, Cranston CL, Oehlerts B, Culbertson M. Data curation: a study of researcher practices and needs. Libraries Acad. (2014) 14:139–64. doi: 10.1353/pla.2014.0009

CrossRef Full Text | Google Scholar

13. National Science Foundation. Press Release 10-077 Scientists Seeking NSF Funding Will Soon be Required to Submit Data Management Plans. (2010). Available online at: http://www.nsf.gov/news/news_summ.jsp?cntn_id=116928 (Accessed 2 October, 2010).

14. European Commission. EC Commission Recommendation of 17.7.2012 on Access to and Preservation of Scientific Information. (2012). Available online at: http://ec.europa.eu/research/science-society/document_library/pdf_06/recommendation-access-and-preservation-scientific-information_en.pdf (Accessed 4 November, 2016).

15. Roche DG, Kruuk LEB, Lanfear R, Binning SA. Public data archiving in ecology and evolution: how well are we doing? PLoS Biol. (2015) 13:e1002295. doi: 10.1371/journal.pbio.1002295

PubMed Abstract | CrossRef Full Text | Google Scholar

16. Vision TJ. Open data and the social contract of scientific publishing. Bioscience (2010) 60:330. doi: 10.1525/bio.2010.60.5.2

CrossRef Full Text | Google Scholar

17. White EP, Baldridge E, Brym ZT, Locey KJ, McGlinn DJ, Supp SR. Nine simple ways to make it easier to (re) use your data. Ideas Ecol Evol. (2013) 6:1–10. doi: 10.4033/iee.2013.6b.6.f

CrossRef Full Text | Google Scholar

18. Fegraus EH, Andelman S, Jones MB, Schildhauer M. Maximizing the value of ecological data with structured metadata: an introduction to ecological metadata language (EML) and principles for metadata creation. Bull Ecol Soc Am. (2005) 86:158–68. doi: 10.1890/0012-9623(2005)86[158:MTVOED]2.0.CO;2

CrossRef Full Text | Google Scholar

19. Robertson T, Dring M, Guralnick R, Bloom D, Wieczorek J, Braak K, et al. The GBIF integrated publishing toolkit: facilitating the efficient publishing of biodiversity data on the internet. PLoS ONE (2014) 9:e102623. doi: 10.1371/journal.pone.0102623

PubMed Abstract | CrossRef Full Text | Google Scholar

20. Oggioni A, Carrara P, Kliment T, Peterseil J, Schentz H. Monitoring of environmental status through long term series: data management system in the EnvEurope project. In: EnviroInfo. Aachen: Shaker Verlag (2012). p. 293–301.

Google Scholar

21. Higgins D, Berkley C, Jones MB. Managing heterogeneous ecological data using Morpho. In: Proceedings of the 14th International Conference on Scientific and Statistical Database Management. IEEE (2002). p. 69–76.

Google Scholar

22. Smirnova L, Mergen P, Groom Q, Wever AD, Penev L, Stoev P, et al. Data sharing tools adopted by the European Biodiversity Observation Network Project. Res Ideas Outcomes (2016) 2:e9390. doi: 10.3897/rio.2.e9390

CrossRef Full Text | Google Scholar

23. Michener WK. Meta-information concepts for ecological data management. Ecol Inform. (2006) 1:3–7. doi: 10.1016/j.ecoinf.2005.08.004

CrossRef Full Text | Google Scholar

24. Roy HE, Preston CD, Harrower CA, Rorke SL, Noble D, Sewell J, et al. GB Non-native Species Information Portal: documenting the arrival of non-native species in Britain. Biol Invasions (2014) 16:2495–505. doi: 10.1007/s10530-014-0687-0

CrossRef Full Text | Google Scholar

25. Pagad S, Genovesi P, Carnevali L, Scalera R, Clout M. IUCN SSC Invasive Species Specialist Group: invasive alien species information management supporting practitioners, policy makers and decision takers. Manage Biol Invasions (2015) 6:127–35. doi: 10.3391/mbi.2015.6.2.03

CrossRef Full Text | Google Scholar

26. Katsanevakis S, Genovesi P, Gaiji S, Hvid HN, Roy H, Nunes AL, et al. Implementing the European policies for alien species: networking, science, and partnership in a complex environment. Manage Biol Invasions (2013) 4:3–6. doi: 10.3391/mbi.2013.4.1.02

CrossRef Full Text | Google Scholar

27. Joppa LN, O'Connor B, Visconti P, Smith C, Geldmann J, Hoffmann M, et al. Filling in biodiversity threat gaps. Science (2016) 352:416–8. doi: 10.1126/science.aaf3565

PubMed Abstract | CrossRef Full Text | Google Scholar

28. Jarnevich CS, Simpson A, Graham JJ, Newman GJ, Bargeron CT. Running a network on a shoestring: the Global Invasive Species Information Network. Manage Biol Invasions (2015) 6:137–46. doi: 10.3391/mbi.2015.6.2.04

CrossRef Full Text | Google Scholar

29. Olenin S, Narius A, Minchin D, David M, Galil B, Gollasch S, et al. Making non-indigenous species information systems practical for management and useful for research: an aquatic perspective. Biol Conserv. (2014) 173:98–107. doi: 10.1016/j.biocon.2013.07.040

CrossRef Full Text | Google Scholar

30. Roy H, Pocock M, Preston C, Roy D, Savage J, Tweddle J, et al. Understanding Citizen Science and Environmental Monitoring: Final Report on Behalf of UK Environmental Observation Framework. NERC/Centre for Ecology and Hydrology (2012).

Google Scholar

31. August T, Harvey M, Lightfoot P, Kilbey D, Papadopoulos T, Jepson P. Emerging technologies for biological recording. Biol J Linnean Soc. (2015) 115:731–49. doi: 10.1111/bij.12534

CrossRef Full Text | Google Scholar

32. Dejean T, Valentini A, Miquel C, Taberlet P, Bellemain E, Miaud C. Improved detection of an alien invasive species through environmental DNA barcoding: the example of the American bullfrog Lithobates catesbeianus. J Appl Ecol. (2012) 49:953–9. doi: 10.1111/j.1365-2664.2012.02171.x

CrossRef Full Text | Google Scholar

33. McGeoch MA, Groom QJ, Pagad S, Petrosyan V, Ruiz G, Wilson J. Data Fitness for Use in Research on Alien and Invasive Species. Copenhagen: GBIF Secretariat (2016). Available online at: http://www.gbif.org/resource/82958

34. Ashburner M, Ball CA, Blake JA, Botstein D, Butler H, Cherry JM, et al. Gene ontology: tool for the unification of biology. Nat Genet. (2000) 25:25–9. doi: 10.1038/75556

PubMed Abstract | CrossRef Full Text | Google Scholar

35. Simpson A, Jarnevich C, Madsen J, Westbrooks R, Fournier C, Mehrhoff L, et al. Invasive species information networks: collaboration at multiple scales for prevention, early detection, and rapid response to invasive alien species. Biodiversity (2009) 10:5–13. doi: 10.1080/14888386.2009.9712839

CrossRef Full Text | Google Scholar

36. Bos B. What Is a Good Standard? An Essay on W3C's Design Principles. (2003). Available online at: https://www.w3.org/People/Bos/DesignGuide/introduction

37. Berendsohn W, Güntsch A, Hoffmann N, Kohlbecker A, Luther K, Müller A. Biodiversity information platforms: from standards to interoperability. ZooKeys (2011) 150:71–87. doi: 10.3897/zookeys.150.2166

CrossRef Full Text | Google Scholar

38. Wieczorek J, Bloom D, Guralnick R, Blum S, Döring M, Giovanni R, et al. Darwin core: an evolving community-developed biodiversity data standard. PLoS ONE (2012) 7:e29715. doi: 10.1371/journal.pone.0029715

PubMed Abstract | CrossRef Full Text | Google Scholar

39. Hulme PE, Bacher S, Kenis M, Klotz S, Kühn I, Minchin D, et al. Grasping at the routes of biological invasions: a framework for integrating pathways into policy. J Appl Ecol. (2008) 45:403–14. doi: 10.1111/j.1365-2664.2007.01442.x

CrossRef Full Text | Google Scholar

40. Essl F, Bacher S, Blackburn TM, Booy O, Brundu G, Brunel S, et al. Crossing frontiers in tackling pathways of biological invasions. Bioscience (2015) 65:769. doi: 10.1093/biosci/biv082

CrossRef Full Text | Google Scholar

41. Pagad S, Hayes K, Katsanevakis S, Costello MJ. World Register of Introduced Marine Species (WRIMS) (2015). Available online at: http://www.marinespecies.org/introduced

42. Convention on Biological Diversity. Pathways of Introduction of Invasive Species, Their Prioritization, and Management (2014). Available online at: http://www.cbd.int/doc/meetings/sbstta/sbstta-18/official/sbstta-18-09-add1-en.pdf

43. Saul WC, Roy HE, Booy O, Carnevali L, Chen HJ, Genovesi P, et al. Assessing patterns in introduction pathways of alien species by linking major invasion data bases. J Appl Ecol. (2017) 54:657–69. doi: 10.1111/1365-2664.12819

CrossRef Full Text | Google Scholar

44. Blackburn TM, Pyšek P, Bacher S, Carlton JT, Duncan RP, Jarošík V, et al. A proposed unified framework for biological invasions. Trends Ecol Evol. (2011) 26:333–9. doi: 10.1016/j.tree.2011.03.023

PubMed Abstract | CrossRef Full Text | Google Scholar

45. Blackburn TM, Essl F, Evans T, Hulme PE, Jeschke JM, Kühn I, et al. A unified classification of alien species based on the magnitude of their environmental impacts. PLoS Biol. (2014) 12:e1001850. doi: 10.1371/journal.pbio.1001850

CrossRef Full Text | Google Scholar

46. McGeoch MA, Genovesi P, Bellingham PJ, Costello MJ, McGrannachan C, Sheppard A. Prioritizing species, pathways, and sites to achieve conservation targets for biological invasion. Biol Invasions (2016) 18:299–314. doi: 10.1007/s10530-015-1013-1

CrossRef Full Text | Google Scholar

47. Hulme PE, Pyšek P, Nentwig W, Vilà M. Will threat of biological invasions unite the European Union? Science (2009) 324:40–1. doi: 10.1126/science.1171111

PubMed Abstract | CrossRef Full Text | Google Scholar

48. Kean J, Tobin P, Lee D, Smith G, Stringer L, Vargas RF, et al. Global Eradication and Response Database (2016). Available online at: http://b3.net.nz/gerda

49. Island Conservation, Coastal Conservation Action Laboratory UCSC, IUCN SSC Invasive Species Specialist Group, University of Auckland and Landcare Research New Zealand. DIISE. The Database of Island Invasive Species Eradications (2015). Available online at: http://diise.islandconservation.org

50. Wilkinson MD, Dumontier M, Aalbersberg IJ, Appleton G, Axton M, Baak A, et al. The FAIR guiding principles for scientific data management and stewardship. Sci Data (2016) 3:160018. doi: 10.1038/sdata.2016.18

PubMed Abstract | CrossRef Full Text | Google Scholar

51. Lucy FE, Roy H, Simpson A, Carlton JT, Hanson JM, Magellan K, et al. INVASIVESNET towards an international association for open knowledge on invasive alien species. Manage Biol Invasions (2016) 7:131–9. doi: 10.3391/mbi.2016.7.2.01

CrossRef Full Text | Google Scholar

52. Faith D, Collen B, Ariño A, Koleff PKP, Guinotte J, Kerr J, et al. Bridging the biodiversity data aps: recommendations to meet users' data needs. Biodiversity Inform. (2013) 8:41–58. doi: 10.17161/bi.v8i2.4126

CrossRef Full Text

53. Borgman CL. The conundrum of sharing research data. J Am Soc Inform Sci Technol. (2012) 63:1059–78. doi: 10.1002/asi.22634

CrossRef Full Text | Google Scholar

54. Donovan C. Introduction: future pathways for science policy and research assessment: metrics vs peer review, quality vs impact. Sci Public Policy (2007) 34:538. doi: 10.3152/030234207X256529

CrossRef Full Text | Google Scholar

55. Taylor J. The assessment of research quality in UK universities: peer review or metrics? Brit J Manage. (2011) 22:202–17. doi: 10.1111/j.1467-8551.2010.00722.x

CrossRef Full Text | Google Scholar

56. Maday C, Moysan M. Records management for scientific data. Arch Manuscripts (2014) 42:190–2. doi: 10.1080/01576895.2014.911686

CrossRef Full Text | Google Scholar

57. Gibney E, Van Noorden R. Scientists losing data at a rapid rate. Nature (2013) 504. doi: 10.1038/nature.2013.14416

CrossRef Full Text

58. Benson DA, Cavanaugh M, Clark K, Karsch-Mizrachi I, Lipman DJ, Ostell J, et al. GenBank. Nucleic Acids Res. (2013) 41:D36. doi: 10.1093/nar/gks1195

PubMed Abstract | CrossRef Full Text | Google Scholar

59. Ribes D, Finholt TA. The long now of technology infrastructure: articulating tensions in development. J Assoc Inform Syst. (2009) 10:375.

Google Scholar

60. Vanderhoeven S, Adriaens T, Desmet P, Strubbe D, Backeljau T, Barbier Y, et al. Tracking Invasive Alien Species (TrIAS): building a data-driven framework to inform policy. Res Ideas Outcomes (2017) 3:e13414. doi: 10.3897/rio.3.e13414

CrossRef Full Text | Google Scholar

61. NOBANIS. Invasive Alien Species: Pathway Analysis and Horizon Scanning for Countries in Northern Europe. Copenhagen: Nordic Council of Ministers (2015).

62. Andow DA. Pathways-based risk assessment of exotic species invasions. In: Carlton J, editor. Invasive Species: Vectors and Management Strategies. Washington, DC: Island Press (2003). p. 439–55.

Google Scholar

63. Rabitsch W, Essl F, Genovesi P, Scalera R. Invasive Alien Species Indicators in Europe-a Review of Streamlining European Biodiversity (SEBI) Indicator 10. EEA-Technical Report, 15/2012 (2012).

64. Armon RH, Zenetos A. Invasive alien species and their indicators. In: Armon RH, Hänninen O, editors. Environmental Indicators. Dordrecht: Springer Netherlands (2015). p. 147–73. doi: 10.1007/978-94-017-9499-2_10

CrossRef Full Text | Google Scholar

65. Rabitsch W, Genovesi P, Scalera R, Biała K, Josefsson M, Essl F. Developing and testing alien species indicators for Europe. J Nat Conserv. (2016) 29:89–96. doi: 10.1016/j.jnc.2015.12.001

CrossRef Full Text | Google Scholar

66. Ficetola GF, Thuiller W, Miaud C. Prediction and validation of the potential global distribution of a problematic alien invasive species—the American bullfrog. Divers Distribut. (2007) 13:476–85. doi: 10.1111/j.1472-4642.2007.00377.x

CrossRef Full Text | Google Scholar

67. Strubbe D, Matthysen E, Graham CH. Assessing the potential impact of invasive ring-necked parakeets Psittacula krameri on native nuthatches Sitta europeae in Belgium. J Appl Ecol. (2010) 47:549–57. doi: 10.1111/j.1365-2664.2010.01808.x

CrossRef Full Text | Google Scholar

68. Jiménez-Valverde A, Peterson AT, Soberón J, Overton J, Aragón P, Lobo JM. Use of niche models in invasive species risk assessments. Biol Invasions (2011) 13:2785–97. doi: 10.1007/s10530-011-9963-4

CrossRef Full Text | Google Scholar

69. Elzinga CL, Salzer DW, Willoughby JW, Gibbs JP. Monitoring Plant and Animal Populations. Malden, MA: Blackwell Science (2001).

Google Scholar

70. Marsh DM, Trenham PC. Current trends in plant and animal population monitoring. Conserv Biol. (2008) 22:647–55. doi: 10.1111/j.1523-1739.2008.00927.x

PubMed Abstract | CrossRef Full Text | Google Scholar

71. Adriaens T, Baert K, Breyne P, Casaer J, Devisscher S, Onkelinx T, et al. Successful eradication of a suburban Pallas's squirrel Callosciurus erythraeus (Pallas 1779) (Rodentia, Sciuridae) population in Flanders (northern Belgium). Biol Invasions (2015) 17:2517–26.

Google Scholar

72. Faulkner KT, Robertson MP, Rouget M, Wilson JR. A simple, rapid methodology for developing invasive species watch lists. Biol Conserv. (2014) 179:25–32. doi: 10.1016/j.biocon.2014.08.014

CrossRef Full Text | Google Scholar

73. Beauchamp VB, Koontz SM, Suss C, Hawkins C, Kyde KL, Schnase JL. An introduction to Oplismenus undulatifolius (Ard.) Roem. & Schult.(wavyleaf basketgrass), a recent invader in Mid-Atlantic forest understories. J Torrey Bot Soc. (2013) 140:391–413. doi: 10.3159/TORREY-D-13-00033.1

CrossRef Full Text | Google Scholar

74. Panzacchi M, Cocchi R, Genovesi P, Bertolino S. Population control of coypu Myocastor coypus in Italy compared to eradication in UK: a cost-benefit analysis. Wildlife Biol. (2007) 13:159–71. doi: 10.2981/0909-6396(2007)13[159:PCOCMC]2.0.CO;2

CrossRef Full Text | Google Scholar

75. Rajmis S, Thiele J, Marggraf RA. Cost-benefit analysis of controlling giant hogweed (Heracleum mantegazzianum) in Germany using a choice experiment approach. NeoBiota (2016) 31:19–41. doi: 10.3897/neobiota.31.8103

CrossRef Full Text | Google Scholar

Keywords: checklists, data interoperability, data management plan, introduced species, non-indigenous, non-native, pest species, standards

Citation: Groom QJ, Adriaens T, Desmet P, Simpson A, De Wever A, Bazos I, Cardoso AC, Charles L, Christopoulou A, Gazda A, Helmisaari H, Hobern D, Josefsson M, Lucy F, Marisavljevic D, Oszako T, Pergl J, Petrovic-Obradovic O, Prévot C, Ravn HP, Richards G, Roques A, Roy HE, Rozenberg M-AA, Scalera R, Tricarico E, Trichkova T, Vercayie D, Zenetos A and Vanderhoeven S (2017) Seven Recommendations to Make Your Invasive Alien Species Data More Useful. Front. Appl. Math. Stat. 3:13. doi: 10.3389/fams.2017.00013

Received: 12 March 2017; Accepted: 15 June 2017;
Published: 30 June 2017.

Edited by:

Aristides Moustakas, Queen Mary University of London, United Kingdom

Reviewed by:

Sarah Supp, University of Wisconsin-Madison, United States
Davide Francesco Tagliapietra, ISMAR-Marine Sciences Institute in Venice (CNR), Italy

Copyright © 2017 Groom, Adriaens, Desmet, Simpson, De Wever, Bazos, Cardoso, Charles, Christopoulou, Gazda, Helmisaari, Hobern, Josefsson, Lucy, Marisavljevic, Oszako, Pergl, Petrovic-Obradovic, Prévot, Ravn, Richards, Roques, Roy, Rozenberg, Scalera, Tricarico, Trichkova, Vercayie, Zenetos and Vanderhoeven. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) or licensor are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Quentin J. Groom, cXVlbnRpbi5ncm9vbUBwbGFudGVudHVpbm1laXNlLmJl

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