Abstract
So far we have mainly dealt with the species problem from an academic perspective—how species notions have evolved historically, what ontological or metaphysical status species have, what species concepts there are and how they differ and why, etc. It was only in the last chapter on species delimitation that taxonomic practice was given more attention, although the focus was on general issues and again theoretical arguments. The main conclusion was that species delimitation will necessarily contain an element of arbitrariness because of the continuousness of the phenomena and processes underlying the origin, distribution and evolution of biodiversity. As a result, the discrete, binary nature of taxonomy (taxon or no taxon) cannot adequately and completely objectively capture and classify diversity at and around the level that we usually think of as species—i.e. the level at and around the tokogeny/phylogeny divide (in sexual organisms) of closely related populations that may or may not be fully interfertile, may or may not merge again or may or may not exchange genetic material shows close phenotypic affinities and sometimes hybrid zones of varying geographical extension and degrees of permeability, etc. Nevertheless, species are commonly viewed as the main currency in many areas of biological research, both applied and theoretical. What impact does the insight that species boundaries cannot be drawn completely objectively have on these disciplines? This will be briefly summarized in the present chapter. The aim is not to provide detailed analyses of how species uncertainty bears on concrete research questions but to give an overview of what is at stake and to sensitize readers to this important issue.
Access this chapter
Tax calculation will be finalised at checkout
Purchases are for personal use only
Notes
- 1.
The name literally means “Ness monster with diamond(-shaped) wing” and is an allusion to its alleged similarity with something like a plesiosaur. Incidentally, it is also an anagram of “monster hoax by Sir Peter S”.
- 2.
That this issue is indeed of practical relevance can be seen, for example, by how seriously the issue of species splitting is taken by the United Nations Environment Programme’s World Conservation Monitoring Centre (UNEP-WCMC 2012). In this document, the recent species splittings in many groups are highlighted, among them primates and bovids.
- 3.
Genetic rescue is the introduction of unrelated individuals into a small and isolated population that is genetically depleted and may show signs of inbreeding depression—with the aim of supporting the local gene pool and decreasing the level of inbreeding. The textbook example is the mountain lion population in Florida (“Florida panther ”). It is usually classified as a distinct subspecies ( Puma concolor coryi) and was on the brink of extinction with serious signs of inbreeding depression (low sperm quality, genital malformations and other symptoms). Finally, in 1995, eight female Texan pumas (P. c. stanleyana) were introduced and the population has recovered well (Johnson et al. 2010). However, there was also opposition to the genetic rescue because it would dilute the original Florida panther gene pool. This opposition (and legal hurdles) would have been even stronger if the Florida panther had been classified as a distinct species, and this may well have resulted in its extinction .
- 4.
Cracraft (1997, p. 325) , incidentally, says: “Phylogenetic species, as basal diagnosable units, are effective functional equivalents of ESUs”.
- 5.
Based on the assumption that the numbers of mature individuals in “Vulnerable” species are evenly distributed throughout the range of possible values for this category (250–1000).
- 6.
In this case it is not an issue of where to draw the line in a continuum, but of an objectively wrong classification because two unrelated lineages were lumped into a polyphyletic species.
- 7.
There are other approaches that result in different areas or regions, of course, but this is irrelevant for our context.
- 8.
A different problem is that even if species taxa across all groups were objective and directly comparable, one group’s diversity in an area may not be representative of that of other groups. While key to the successful protection of overall biodiversity, this issue is not relevant to our present topic as it regards intergroup differences in diversity distribution but not the delimitation of species.
- 9.
Divergent and phylogenetically isolated in this case means that the summed branch length to a species’ sister taxon is very high. Branch lengths can of course be measured differently, but ultimately they are a function of time to common ancestors.
- 10.
Fortunately, the above-mentioned biodiversity hotspots do not only harbour extraordinarily high numbers of species but seem to also harbour high levels of evolutionary history or phylogenetic diversity (Sechrest et al. 2002).
- 11.
I am not considering the fact that many could also be split further within Eurasia and North America, respectively, which adds to the taxonomic uncertainty.
- 12.
Just a few comments here. The three-toed woodpecker is an example where recently splitting has been suggested such that only the Eurasian populations go by the name of Picoides tridactylus, while the American three-toed woodpecker is called P. dorsalis (Zink et al. 2002). Grey and great blue herons are usually considered two species ( Ardea cinerea and A. herodias), while wolves ( Canis lupus) and brown bears ( Ursus arctos ) are considered conspecific. Red deer and wapiti used to be classified as the same species, but recently splitting into two species ( Cervus elaphus and C. canadensis) has been more common. The important point here is not so much what the common taxonomic view is at any one time, but rather that for the majority of these taxa pairs both splitting and lumping could be argued for, depending on the criteria that one considers most relevant.
- 13.
In a study of European red deer, we have done exactly this (Zachos et al. 2016), and the bottlenecked and threatened populations/subspecies of red deer on Sardinia and in Mesola were found to exhibit by far the lowest values, often one or even two orders of magnitude lower than those for other populations. Still, the absolute numbers may not be very reliable.
References
Agapow P-M, Sluys R (2005) The reality of taxonomic change. Trends Ecol Evol 20:278–280
Agapow P-M, Bininda-Emonds ORP, Crandall KA, Gittleman JL, Mace GM, Marshall JC, Purvis A (2004) The impact of species concept on biodiversity studies. Q Rev Biol 79:161–179
Allmon WD (1992) Genera in paleontology: definition and significance. Hist Biol 6:149–158
Bertrand Y, Pleijel F, Rouse GW (2006) Taxonomic surrogacy in biodiversity assessments, and the meaning of Linnaean ranks. Syst Biodivers 4:149–159
Cadotte MW, Davies TJ, Regetz J, Kembel SW, Cleland E, Oakley TH (2010) Phylogenetic diversity metrics for ecological communities: integrating species richness, abundance and evolutionary history. Ecol Lett 13:96–105
Cracraft J (1997) Species concepts in systematics and conservation biology – an ornithological viewpoint. In: Claridge MF, Dawah HA, Wilson MR (eds) Species: the units of biodiversity. Chapman & Hall, London, pp 325–339
Daugherty CH, Cree A, Hay JM, Thompson MB (1990) Neglected taxonomy and continuing extinctions of tuatara (Sphenodon). Nature 347:177–179
Davies TJ, Cadotte MW (2011) Quantifying biodiversity: does it matter what we measure? In: Zachos FE, Habel JC (eds) Biodiversity hotspots. Distribution and protection of conservation priority areas. Springer, Berlin, pp 43–60
Doolittle WF, Zhaxybayeva O (2009) On the origin of prokaryotic species. Genome Res 19:744–756
Faith DP (1992) Conservation evaluation and phylogenetic diversity. Biol Conserv 61:1–10
Faurby S, Eiserhardt WL, Svenning J-C (2016) Strong effect of variation in taxonomic opinion on diversification analyses. Methods Ecol Evol 7:4–13
Frankham R, Ballou JD, Dudash MR, Eldridge MDB, Fenster CB, Lacy RC, Mendelson JR III, Porton IJ, Ralls K, Ryder OA (2012) Implications of different species concepts for conserving biodiversity. Biol Conserv 153:25–31
Garnett ST, Christidis L (2007) Implications of changing species definitions for conservation purposes. Bird Conserv Int 17:187–195
Geist V (1992) Endangered species and the law. Nature 357:274–276
Gotelli NJ, Colwell RK (2011) Estimating species richness. In: Magurran AE, McGill BJ (eds) Biological diversity. Frontiers in measurement and assessment. Oxford University Press, Oxford, pp 39–54
Gould SJ (1989) Wonderful life. The Burgess Shale and the nature of history. W. W. Norton, New York
Groves CP (2014) Primate taxonomy: inflation or real? Annu Rev Anthropol 43:27–36
Gutiérrez EE, Helgen KM (2013) Outdated taxonomy blocks conservation. Nature 495:314
Haig SM, Beever EA, Chambers SM, Draheim HM, Dugger BD, Dunham S, Elliott-Smith E, Fontaine JB, Kesler DC, Knaus BJ, Lopes IF, Loschl P, Mullins TD, Sheffield LM (2006) Taxonomic considerations in listing subspecies under the U.S. Endangered Species Act. Conserv Biol 20:1584–1594
Harris DJ, Froufe E (2005) Taxonomic inflation: species concept or historical geopolitical bias? Trends Ecol Evol 20:6–7
Hendry AP, Vamosi SM, Latham SJ, Heilbuth JC, Day T (2000) Questioning species reality. Conserv Genet 1:67–76
Hey J (2001a) Genes, categories, and species. The evolutionary and cognitive causes of the species problem. Oxford University Press, Oxford
Hey J (2001b) The mind of the species problem. Trends Ecol Evol 16:326–329
Heywood VH (1998) The species concept as a socio-cultural phenomenon – a source of the scientific dilemma. Theor Biosci 117:203–212
Isaac NJB, Mallet J, Mace GM (2004) Taxonomic inflation: its influence on macroecology and conservation. Trends Ecol Evol 19:464–469
Isaac NJB, Mace GM, Mallet J (2005) Response to Agapow and Sluys: The reality of taxonomic change. Trends Ecol Evol 20:280–281
Isaac NJB, Turvey ST, Collen B, Waterman C, Baillie JEM (2007) Mammals on the EDGE: conservation priorities based on threat and phylogeny. PLoS One 2(3):e296
Johnson WE, Onorato DP, Roelke ME, Land ED, Cunningham M, Belden RC, McBride R, Jansen D, Lotz M, Shindle D, Howard J, Wildt DE, Penfold LM, Hostetler JA, Oli MK, O’Brien SJ (2010) Genetic restoration of the Florida panther. Science 329:1641–1645
Knapp S, Lughadha EN, Paton A (2005) Taxonomic inflation, species concepts and global species lists. Trends Ecol Evol 20:7–8
Luikart G, Ryman N, Tallmon DA, Schwartz MK, Allendorf FW (2010) Estimation of census and effective population sizes: the increasing usefulness of DNA-based approaches. Conserv Genet 11:355–373
Mace GM (2004) The role of taxonomy in species conservation. Philos Trans R Soc Lond B 359:711–719
Magurran AE (2004) Measuring biological diversity. Blackwell, Malden
Mallet J, Isaac NJB, Mace GM (2005) Response to Harris and Froufe, and Knapp et al.: Taxonomic inflation. Trends Ecol Evol 20:8–9
Marris E (2007) The species and the specious. Nature 446:250–253
May RM (1990) Taxonomy as destiny. Nature 347:129–130
McCormack JE, Maley JM (2015) Interpreting negative results with taxonomic and conservation implications: another look at the distinctness of coastal California gnatcatchers. Auk 132:380–388
Meijaard E, Nijman V (2003) Primate hotspots on Borneo: predictive value for general biodiversity and the effects of taxonomy. Conserv Biol 17:725–732
Mittermeier RA, Turner WR, Larsen FW, Brooks TM, Gascon C (2011) Global biodiversity conservation: the critical role of hotspots. In: Zachos FE, Habel JC (eds) Biodiversity hotspots. Distribution and protection of conservation priority areas. Springer, Berlin, pp 3–22
Morrison WR III, Lohr JL, Duchen P, Wilches R, Trujillo D, Mair M, Renner SS (2009) The impact of taxonomic change on conservation: does it kill, can it save, or is it just irrelevant. Biol Conserv 142:3201–3206
Myers N, Mittermeier RA, Mittermeier CG, da Fonseca GAB, Kent J (2000) Biodiversity hotspots for conservation priorities. Nature 403:853–858
Noss RF, Platt WJ, Sorrie BA, Weakley AS, Means DB, Costanza J, Peet RK (2015) How global biodiversity hotspots may go unrecognized: lessons from the North American Coastal Plain. Divers Distrib 21:236–244
O’Brien SJ, Mayr E (1991) Bureaucratic mischief: recognizing endangered species and subspecies. Science 251:1187–1188
Peterson AT, Navarro-Sigüenza AG (1999) Alternate species concepts as bases for determining priority conservation areas. Conserv Biol 13:427–431
Riddle BR, Hafner DJ (1999) Species as units of analysis in ecology and biogeography: time to take the blinders off. Global Ecol Biogeogr 8:433–441
Scott P, Rines R (1975) Naming the Loch Ness monster. Nature 258:466–468
Sechrest W, Brooks TM, da Fonseca GAB, Konstant WR, Mittermeier RA, Purvis A, Rylands AB, Gittleman JL (2002) Hotspots and the conservation of evolutionary history. Proc Natl Acad Sci USA 99:2067–2071
Senn H, Banfield L, Wacher T, Newby J, Rabeil T, Kaden J, Kitchener AC, Abaigar T, Silva TL, Maunder M, Ogden R (2014) Splitting or lumping? A conservation dilemma exemplified by the critically endangered dama gazelle (Nanger dama). PLoS One 9(6):e98693
Stanley SM (1979) [1998] Macroevolution – pattern and process. Johns Hopkins University Press, Baltimore, MD
UNEP-WCMC (2012) Fauna: new species and other taxonomic changes relating to species listed in the EC wildlife trade regulations. A report to the European Commission. UNEP-WCMC, Cambridge
Vane-Wright RI, Humphries CJ, Williams PH (1991) What to protect? Systematics and the agony of choice. Biol Conserv 55:235–254
Vellend M, Cornwell WK, Magnuson-Ford K, Mooers AØ (2011) Measuring phylogenetic biodiversity. In: Magurran AE, McGill BJ (eds) Biological diversity. Frontiers in measurement and assessment. Oxford University Press, Oxford, pp 194–207
Williams KJ, Ford A, Rosauer DF, De Silva N, Mittermeier R, Bruce C, Larsen FW, Margules C (2011) Forests of East Australia: the 35th biodiversity hotspot. In: Zachos FE, Habel JC (eds) Biodiversity hotspots. Distribution and protection of conservation priority areas. Springer, Berlin, pp 295–310
Wisdom MJ, Mills LS (1997) Sensitivity analysis to guide population recovery: prarie chickens as an example. J Wildlife Manage 61:302–312
Zachos FE, Clutton-Brock TH, Festa-Bianchet M, Lovari S, Macdonald DW, Schaller GB (2013b) Species splitting puts conservation at risk. Nature 494:35
Zachos FE, Frantz AC, Kuehn R, Bertouille S, Colyn M, Niedzialkowska M, Pérez-González J, Skog A, Sprĕm N, Flamand M-C (2016) Genetic structure and effective population sizes in European red deer (Cervus elaphus) at a continental scale: insights from microsatellite DNA. J Hered 107:318–326
Zink RM, Barrowclough GF, Atwood JL, Blackwell-Rago RC (2000) Genetics, taxonomy, and conservation of the threatened California gnatcatcher. Conserv Biol 14:1394–1405
Zink RM, Rohwer S, Drovetski S, Blackwell-Rago RC, Farrell SL (2002) Holarctic phylogeography and species limits of three-toed woodpeckers. Condor 104:167–170
Zink RM, Groth JG, Vázquez-Miranda H, Barrowclough GF (2013) Phylogeography of the California gnatcatcher (Polioptila californica) using multilocus DNA sequences and ecological niche modeling: implications for conservation. Auk 130:449–458
Author information
Authors and Affiliations
Rights and permissions
Copyright information
© 2016 Springer International Publishing Switzerland
About this chapter
Cite this chapter
Zachos, F.E. (2016). The Practical Relevance of Species Concepts and the Species Problem. In: Species Concepts in Biology. Springer, Cham. https://doi.org/10.1007/978-3-319-44966-1_7
Download citation
DOI: https://doi.org/10.1007/978-3-319-44966-1_7
Published:
Publisher Name: Springer, Cham
Print ISBN: 978-3-319-44964-7
Online ISBN: 978-3-319-44966-1
eBook Packages: Biomedical and Life SciencesBiomedical and Life Sciences (R0)