A Census of Marine Biodiversity Knowledge, Resources, and Future Challenges
By Mark John Costello, Marta Coll, Roberto Danovaro, Patrick N. Halpin, H. Ojaveer, P. Miloslavich. PLoS ONE, 2010
641 citations recorded by the source corpus.
The resources available for research are always limited. When setting priorities for research funding, governments, industry, and funding agencies must balance the demands of human health, food supply, and standards of living, against the less-tangible benefits of discovering more about the planet's biodiversity. Scientists have discovered almost 2 million species indicating that we have made great gains in our knowledge of biodiversity. However, this knowledge may distract attention from the estimated four-fifths of species on Earth that remain unknown to science, many of them inhabiting our oceans [1], [2]. The world's media still find it newsworthy when new species are discovered [1]. However, the extent of this taxonomic challenge no longer appears to be a priority in many funding agencies, perhaps because society and many scientists believe we have discovered most species, or that doing so is out of fashion except when new technologies are employed. Another symptom of this trend may be that the increased attention to novel methods available in molecular sciences is resulting in a loss of expertise and know-how in the traditional descriptive taxonomy of species [3]. The use of molecular techniques complements traditional methods of describing species but has not significantly increased the rate of discovery of new species (at least of fish), although it may help classify them [4]. At least in Europe, there was a mismatch between the number of species in a taxon and the number of people with expertise in it [5]. Unfortunately, because most species remain to be discovered in the most species-rich taxa [2], [5], [6], [7], there are then few experts to appreciate that this work needs to be done. Evidently, a global review of gaps in marine biodiversity knowledge and resources is overdue. History of discovering marine biodiversity Although the economic exploitation of marine resources dates back to prehistoric times, and historical documentation has existed since the third century B.C. with Aristotle's contributions in the Mediterranean Sea (e.g. [8]), the establishment of systematic collections of marine organisms began only during the seventeenth and eighteenth centuries. Global marine biodiversity investigations at these times depended not only on the availability of expertise, but also on foreign policies of the colonial powers of the time. For those reasons, the specimens collected from several regions (e.g., Caribbean, Japan, South America, Africa) were mostly brought to Europe, where they were described, deposited in museum collections, and used for the production of marine biological monographs. These early publications contained descriptions and checklists of many marine species, such as molluscs, crustaceans, fishes, turtles, birds, and mammals (e.g. [9], [10], [11]). The history of research on marine biodiversity can generally be divided into three periods: early exploratory studies, local coastal “descriptive” studies, and large-scale multidisciplinary investigations and syntheses. These periods vary in timing by different seas and countries. The first exploratory studies in several regions (e.g., South America, Caribbean, South Africa, Pacific Ocean) took place from the mid-1700s until the late-1800s, in association with mainly European, North American, and Russian exploration expeditions, such as the Kamchatka Expedition in the 1740s, James Cook's voyages in the 1770s, the cruise of HMS Beagle in the 1830s, the voyage of HMS Challenger in the 1870s, and the first deep-sea investigations in the Mediterranean Sea [8], [9], [12], [13]. Pioneer investigations on deep-sea organisms were conducted in the Aegean Sea, where Forbes [14] noticed that sediments became progressively more impoverished in terms of biodiversity with increasing sampling depth. The azoic hypothesis proposed by Forbes suggested that life would be extinguished beyond 500 m depth, although a work published 68 years earlier provided indisputable evidence of the presence of life in the Gulf of Genoa at depths down to 1,000 m [15]. The taxonomists who described marine species at these times seldom collected specimens themselves in the field and, therefore, had only second-hand information about the distribution and ecology of the samples they received [4], [8]. Some of the early descriptions of tropical species thus do not even have the locality where the holotype or voucher material was collected (some examples in Chenu 1842–1853). The second period of regional studies was initiated by enhanced availability of research resources (experts, institutes, and vessels) in developing countries around the mid-1900s. The earliest institutions and research stations, many of which continue to operate, were founded in some areas as early as the late 1800s and early 1900s (e.g. [11], [16], [17]). Wide-scale establishment of laboratories in several continents (Europe, New Zealand, North and South America) have only been operational since the 1950s–1960s. The third stage, large-scale multidisciplinary investigations, has evolved since the 1990s, and is related to development and application of modern technologies and implementation of large, multinational research projects. Perhaps the largest of such investigations was the Census of Marine Life (Census).
Subfields: Ecology, Global and Planetary Change
View Paper: https://www.semanticscholar.org/paper/1e61ed8724dae78a2b48d2df2cb1b88de7ea976d
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In Ecology
- Marta Coll
- Daniel Pauly
- Wwl Cheung
- R. Watson
- V. Karpouzi
- Villy Christensen
- Joan Navarro
- Argyro Zenetos
In Global and Planetary Change
Citations in the corpus
- Acoustic fish communities: sound diversity of rocky habitats reflects fish species diversity (2019, background): “…human livelihoods and well-being as well as water quality (Pauly et al. 2005), but it is facing substantial losses due to multiple cumulative human impacts on ecosystems, including overfishing, pollution and climate change (Sala & Knowlton 2006, Costello et al. 2010, Micheli et al. 2013).”
- The Mediterranean Sea under siege: spatial overlap between marine biodiversity, cumulative threats and marine reserves (2012, background): “…and degradation, as well as extraction, pollution, eutrophication and the introduction of alien species, and recently climate change, are the most important threats that affect the greatest number of taxonomic groups occurring in the Mediterranean Sea (Coll et al., 2010; Costello et al., 2010).”
- DNA metabarcoding in diet studies: Unveiling ecological aspects in aquatic and terrestrial ecosystems (2019, background): “Secondly, aquatic environments hold thousands of vertebrate species (Balian et al., 2008; Costello et al., 2010), with a large fraction estimated to remain undescribed (e.g., Mora, Tittensor, Adl, Simpson, & Worm, 2011) and tens of new species being described every year (WoRMS Editorial Board,…”
- Fifty years on: Lessons from marine reserves in New Zealand and principles for a worldwide network (2014, background): “We have not yet discovered all the species in any geographic region, including New Zealand (Gordon et al., 2010; Costello et al., 2010, 2012).”
- The destruction of the 'animal forests' in the oceans: Towards an over- simplification of the benthic ecosystems (2013, background): “Today habitat loss has been identified as the leading problem faced by species and ecosystem conservation in the oceans (Costello et al., 2010), and its poor management is partly due to our ignorance and common use of large areas that are governed by different rules than the land areas.”
- Dynamics of biological invasions and pathways over time: a case study of a temperate coastal sea (2017, background): “Invasions by non-indigenous species (NIS) are acknowledged as a major external stressor of change in marine ecosystems globally (e.g. Costello et al. 2010) and should be addressed along with climate change, exploitation of living resources, eutrophication and habitat destruction (Edelist et al.…”
- Building capacity in biodiversity monitoring at the global scale (2017, background): “The ten-year global Census of Marine Life programme improved access to data on marine life, and identified unexplored regions and knowledge gaps (Costello et al. 2010, 2013a, b, 2015, 2017).”
- Predicting the number of known and unknown species in European seas using rates of description (2011, background): “A recent analysis across 24 regions of the world, found that the relative number of marine species across phyla and classes was variable, although whether this reflected different evolution of biota or bias in taxonomic effort and knowledge is as yet unclear (Costello et al., 2010).”
- The magnitude of global marine species diversity. (2012, background): “The relative species richness of higher taxa varies across geographic regions [46], although whether this is true or reflects variation in sampling and taxonomic effort is unclear.”
- Alien species in the Mediterranean Sea by 2010. A contribution to the application of European Union's Marine Strategy Framework Directive (MSFD). Part I. Spatial distribution (2010, background): “Compared to the latest lists of alien biota (COLL et al., 2010; COSTELLO et al., 2010) the present work includes a larger number (954) of species (Table 4).”
- A Catalogue of Marine Biodiversity Indicators (2016, background): “…zones host characteristic communities and species, entangled within unique ecological processes that require specific sampling and assessment approaches (Costello et al., 2010; Danovaro et al., 2014; Thurber et al., 2014; Rogers, 2015) and, therefore, specific indicators for assessing their status.”
- Extensive gaps and biases in our knowledge of a well‐known fauna: implications for integrating biological traits into macroecology (2012, neutral): “This fauna is especially well documented in terms of its biogeography and taxonomy (Costello et al., 2010), thanks to a long history of marine biological research (e.”