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Corresponding author: Javier Loidi ( javier.loidi@ehu.eus ) Academic editor: Arkadiusz Nowak
© 2023 Javier Loidi.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Loidi J (2023) Syntaxonomic ranks, biogeography and typological inflation. Vegetation Classification and Survey 4: 1285-290. https://doi.org/10.3897/VCS.101648
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To reduce the typological inflation observed in some territories where intensive phytosociological studies have been carried out and numerous descriptive papers have been published, an outline of the biogeographical amplitude of the different syntaxonomic ranks is proposed. Phytosociological classes are divided into five main vegetation clusters: 1. Zonal vegetation, determined mainly by climatic conditions; 2. Azonal coastal and saline vegetation; 3. Azonal rocky vegetation; 4. Azonal wetland and aquatic vegetation; 5. Highly disturbed anthropogenic vegetation. In each of these, the various ranks (class, order, alliance, association and subassociation) have a particular range which is expressed by the biogeographical territory in which they most likely occur. This area can refer to different respective categories: kingdom, region, province, sector and district. Some additional comments about typological inflation are made in order to focus on two phenomena: desire for fame and geographic drift.
alliance, association, biogeographical territories, class, desire for fame, order, subassociation, typological inflation
After an entire century of the Braun-Blanquet approach being applied to classify vegetation in several regions of the world, most intensely in Europe, it is interesting to reflect on the patterns of territorial scope in the geographic distribution of the different syntaxonomic units in order to unify criteria for their description and acceptance. In relation to this, it is convenient to highlight some observable negative aspects in the practice of describing new syntaxa lacking unified criteria. Several improvements in the application of this approach have recently been introduced (
It is important not to forget that the application of Braun-Blanquet’s floristic-ecological approach requires a high level of knowledge of the surveyed region’s flora, which has delayed its expansion in countries outside Europe and other areas where floristic knowledge is insufficient. However, the high diagnostic value of the described units, based on their intrinsic compositional content, make it an unrivalled approach as it is based on an essential attribute of the plant community. It is also invaluable in the assessment of biodiversity and in designing accurate and scientifically sound conservation policies. In addition, a hierarchical typology (syntaxonomy) allows the use of best-fit unit ranks for different levels of territorial division.
It is essential to retain rigorous criteria in defining and describing syntaxa, which must correspond to a clear systematic arrangement. Therefore, researchers should strictly follow the criteria and definitions of the system’s founders and consider some suggested biogeographical indications. The basic conceptions on syantaxa have been extracted from the classic literature describing this topic, i.e.
The development of the Braun-Blanquet approach, mainly in Europe, but also in other parts of the world, has produced an enormous accumulation of information, which is now stored in large datasets, opening the way to highly efficient data management and analysis (
Some time ago, the phenomenon of intense publication of new units, often in local studies, was termed “typological inflation” by
It has become clear that these recommendations were not optimally followed, and the description of new syntaxa has not been controlled by objective and universal criteria. This was the case both in many descriptive local surveys and in some of the checklists summarizing the plant communities of certain regions. Unfortunately, this tendency still continues in some regions, leading to the humorous note that more associations than species have been described.
Since phytosociology seeks to establish a universal typology of plant communities, it is necessary to respect homogeneity of the criteria when describing new syntaxa, as was recommended by
Two main reasons can be highlighted for this inflationary trend:
Desire for fame
. Authors who describe a new syntaxon are “rewarded” with the authorship of the described unit at the end of its name, giving satisfaction to a certain vanity, which is not a rare feeling among scientists (
Geographic drift. This phenomenon could also explain a part of the inflation. Within the geographic range of an association, there may be subareas in which particular taxa occur that are absent in others. If these plants are forming distinct species combination of the syntaxon, there is the possibility to describe a local subassociation or even a new association separated from the original one. However, these geographically distinct taxa might have the optimum of occurrence in other vegetation types and appear only as companions in our surveyed sub- or association. It is the case of using stenochorous species of the seral stages, scrub or grassland communities, as differential species of a new forest association. One example of this could be the recently published forest association Glandoro diffusae-Quercetum fagineae (
For the coherence of the hierarchical system that describes the vegetation of a given territory, we should seek for a broad consensus on the conditions that the units of different rank must meet in order to be accepted by the scientific community. The criteria set out in the aforementioned literature should dominate this process, avoiding the unnecessary description of units outside the orthodoxy of the method. To reinforce these criteria, some indications are given about the biogeographical arguments that should be considered. This additional biogeographical perspective aims to achieve a homogeneity in the criteria for establishing and accepting new units.
In Table
The main biogeographical units considered here are as follows: Kingdom, Region, Province, Sector and District. Subordinate units such as Subkingdom, Subregion, Subprovince, Subsector and Subdistrict may be considered, too. They have been established based on their floristic (
Scheme of the approximate biogeographic amplitude of the syntaxonomic ranks within each vegetation type in the western European vegetation (
Syntaxonomic rank | Vegetation types | Biogeographic rank | |||||
---|---|---|---|---|---|---|---|
District | Sector | Province | Region | Kingdom | Subcosmopolitan | ||
subassociation | 1. zonal | xx | xx | ||||
2. Azonal coastal saline | xx | xx | |||||
3. Azonal rocky | xx | xx | |||||
4. Azonal wetland | xx | ||||||
5. Disturbed | xx | ||||||
Association | 1. Zonal | xx | |||||
2. Azonal coastal saline | xx | ||||||
3. Azonal rocky | xx | xx | |||||
4. Azonal wetland | xx | xx | |||||
5. Disturbed | xx | ||||||
Alliance | 1. Zonal | xx | xx | ||||
2. Azonal coastal saline | xx | ||||||
3. Azonal rocky | xx | ||||||
4. Azonal wetland | xx | ||||||
5. Disturbed | xx | ||||||
Order | 1. Zonal | xx | |||||
2. Azonal coastal saline | xx | xx | |||||
3. Azonal rocky | xx | xx | |||||
4. Azonal wetland | xx | ||||||
5. Disturbed | xx | ||||||
Class | 1. Zonal | xx | xx | ||||
2. Azonal coastal saline | xx | xx | |||||
3. Azonal rocky | xx | xx | |||||
4. Azonal wetland | xx | xx | |||||
5. Disturbed | xx | xx |
The association is the fundamental unit of the system, similar to the species in botanical systematics. It is recognised by the characteristic species combination (charakteristische Artenkombination) and mainly by its characteristic species, as stated by
Each association must correspond to a habitat type occupying a well-defined biotope in a clearly defined territory (biogeography). Its characteristic species combination should be restricted to the plants that essentially constitute the community, overlooking, for diagnostic purposes, plants originating from other vegetation types occurring in the vicinity and entering the plot as companions. Elements not belonging to the considered vegetation type (e.g., deciduous wood in relation to fringe vegetation or grasslands) should not be considered good diagnostic taxa.
In the last decades, most of the described and accepted associations , mainly in Europe, are based on the characteristic species combination, rarely on characteristic taxa (
Looking at the concepts posed by the above mentioned authors, the association has to have a combination of species which repeats across its range as well as a defined set of ecological requirements. Its area of occurrence is determined by the habitat type it describes, usually a moderate extent in the case of zonal vegetation. Climatically delimited forests, shrublands, scrub, crevices, and scree associations have often a narrow distribution, often a biogeographical sector or subprovince (e.g., associations within Quercetea ilicis: Lauro nobilis-Quercetum ilicis – eastern Cantabrian: Santanderian Biscayan district; Querco-Fagetea: Pteridio aquilini-Quercetum pubescentis – Eastern Pyrenees: eastern Pyrenean subsector; Ononido-Rosmarinetea: Erico multiflorae-Lavanduletum dentatae – South Valencia: Setabense sector). Some other vegetation types which harbour many endemics can have even narrower ranges such as the district or the sector (Asplenietea trichomanis: Centrantho lecoquii-Saxifragetum canaliculatae – Orocantabrian: Picoeuropean sector; Thlaspietea rotundifolii: Rumici scutati-Aquilegietum cazorlensis – Cazorla range: Subbetic sector; etc.). A much wider distribution, often a province, corresponds to disturbed vegetation, such as intensely grazed grasslands, nitrophilous vegetation or weed communities (associations of Molinio-Arrhenatheretea: Malvo moschatae-Arrhenatheretum bulbosi, Galio-Urticetea: Aegopodio-Menthetum longifoliae, etc.). Similarly, vegetation types associated with water, such as fens, have a large distribution, usually a province or region (associations of Phragmito-Magnocaricetea: Typhetum angustifoliae, Potametea: Nupharetum pumilae, etc.). This is proportional to the abundance of stenochorous taxa in each of the environments concerned. The Mediterranean scrubs, cliffs and screes are rich in endemics, while aquatic habitats and severely disturbed anthropic communities rarely host such species. This is likely related to the isolation phenomena, the ancestors of the former floristic groups experienced in their evolutionary history, combined with their poor dispersal abilities.
The subassociation is comparable to the subspecies and it is also defined by a species combination and distinguished only by differential species. There can be geographic and ecological (transitional) subassociations. Their range can correspond to a district or sector.
The associations having evident floristic-ecological affinities and occupying similar habitats in neighbouring territories form an alliance. As a broader unit than association, alliances have an evolutionary and biogeographical meaning as they have characteristic species (at least one) (
The order gathers similar alliances and has a broader scope in terms of ecology and area. It has a higher number of characteristic taxa than the alliances. For instance, the order Fagetalia gathers several alliances of deciduous temperate forests in Europe. The distribution of an order is broader, often a province or group of provinces (region), or even a kingdom in coastal vegetation. It may be considered that the criteria for defining an order are similar to those for the class (
It is the supreme rank of the system that gathers one or several orders, characterised by a set of characteristic plant taxa. In the European tradition, there is an implicit consensus to maintain the traditional class typology as far as reasonably possible. Thus, general vegetation studies are quite conservative on this point (
The class is the most controversial unit of synsystematics, and several contributions have tried to clarify what a phytosociological class is (
The problem of inflation in syntaxonomy comes from an often narrow perspective that does not take biogeographical context into account when describing new vegetation types. This is particularly important in areas which have had intensive surveys over a long period of time. Sometimes, this excessive numerosity of defined syntaxa is a reflection of rash and ill-considered decisions or a lack of comparative phytosociological data. It is therefore important for future phytosociological studies, besides maintaining excellent research standards and high quality data sampling and management, to provide not only a reliable and accurate species composition and ecology when defining new vegetation units, but also to take into account the biogeographical aspects of the newly defined syntaxa.