Life form classification follows the system of Raunkiaer (1934), which is based on the position of the buds that survive the unfavourable season. Macrophanerophytes are woody plants that bear the surviving buds at least 2 m above the ground, usually trees; nanophanerophytes are woody plants with surviving buds 0.3–2 m above the ground, usually shrubs; chamaephytes are herbs or low woody plants with surviving buds above the ground, but not more than 30 cm above it; hemicryptophytes are perennial or biennial herbs with surviving buds on aboveground shoots at the level of the ground; geophytes are perennial plants with surviving buds belowground, usually with bulbs, tubers or rhizomes; hydrophytes are plants with surviving buds in water, usually on the bottom of water bodies; therophytes are summer- or winter-annual herbs that survive the unfavourable season only as seeds germinating in autumn, winter or spring.
The data on life forms were taken from the Key to the Flora of the Czech Republic (Kaplan et al. 2019). Newly added alien taxa were assigned to the categories of life forms based on the FloraVeg.EU database (Dřevojan et al. 2022). Some taxa can belong to more than one life form. In such cases, the dominant life form is listed first.
Kaplan Z., Danihelka J., Chrtek J. Jr., Kirschner J., Kubát K., Štěpánek J. & Štech M. (eds) (2019) Klíč ke květeně České republiky [Key to the flora of the Czech Republic]. Ed. 2. – Academia, Praha.
Dřevojan P., Čeplová N., Štěpánková P. & Axmanová I. (2022) Life form. – www.FloraVeg.EU.
Raunkiaer C. (1934) The life forms of plants and statistical plant geography. – Clarendon Press, Oxford.
Flower colour is reported for nearly all angiosperms except duckweeds (Araceae p. p.) and some hybrids for which data on flower colour were not available.
If a species has more than one flower colour, all colours are reported irrespective of their frequency. This approach is used both for species that regularly form populations with different flower colours (e.g. Corydalis cava and Iris pumila) and for species with occasional occurrence of deviating flower colour (e.g. albinism in Salvia pratensis or pink flowers in Ajuga reptans). However, the whole range of variation is not fully reported in cultivated plants, for which some cultivars of different colour may be ignored (e.g. Gladiolus hortulanus and Callistephus chinensis). In plants with flowers of two colours (e.g. Cypripedium calceolus), both colours are reported. In plants with multi-coloured flowers (e.g. the variegated lip in Ophrys apifera) the predominant colour is reported.
If the flower has a well-developed perianth, the reported flower colour relates to the corolla or the tepals of the homochlamydeous perianth. If such a flower has bracts of a contrasting colour (e.g. Melampyrum nemorosum), their colour is not considered. If the corolla or the homochlamydeous perianth is not developed, the flower colour is based on the calyx (e.g. Daphne mezereum), bracts (e.g. Aristolochia clematitis), the system of bracts and bracteoles in the inflorescence (Euphorbia) or the involucre on secondary peduncles (Bupleurum longifolium). In species of Araceae with spadix and spathe of contrasting colours (e.g. Calla palustris) both colours are reported. The colour of the whole inflorescence is reported for some plants with reduced flowers (e.g. Betula, Salix, some Cyperaceae and Typhaceae). Spikelets in Poaceae are reported as green disregarding a possible violet tint; exceptions include the Melica ciliata agg. and Cortaderia that are reported as white. Also in other, rare cases, the inflorescence colour is reported as flower colour (e.g. green in Ficus carica). In Asteraceae, the colours of the disk flowers and ray flowers are reported separately if the ray flowers are developed and have a contrasting colour (e.g. Bellis perennis). The colour of the involucrum is reported for species with tiny flower heads and indistinct flowers (e.g. Artemisia campestris and Xanthium) and for “immortelles” (e.g. Helichrysum and Xeranthemum).
Information on flower colour is partly based on the field knowledge, partly obtained from various photographs and descriptions in the Flora of the Czech Republic (vols. 1–8; Hejný et al. 1988–1992, Slavík et al. 1997–2004, Štěpánková et al. 2010). In the taxa that are not reported in the Flora of the Czech Republic, as well as in unclear cases (especially in alien species), other sources were used, especially the Flora of North America (Flora of North America Editorial Committee 1993), the Flora of China (Wu et al. 1994) and the Flora of Pakistan (http://www.tropicos.org/Project/Pakistan).
Categories
Štěpánková P. & Grulich V. (2019) Flower colour. – www.pladias.cz.
Flora of North America Editorial Committee (eds) (1993) Flora of North America North of Mexico. – Oxford
University Press, New York.
Flora of Pakistan. – http://www.tropicos.org/Project/Pakistan
Hejný S., Slavík B., Chrtek J., Tomšovic P. & Kovanda M. (eds) (1988) Květena České socialistické republiky [Flora of the Czech Socialist Republic]. Vol. 1. – Academia, Praha.
Hejný S., Slavík B., Hrouda L. & Skalický V. (eds) (1990) Květena České republiky [Flora of the Czech Republic]. Vol. 2. – Academia, Praha.
Hejný S., Slavík B., Kirschner J. & Křísa B. (eds) (1992) Květena České republiky [Flora of the Czech Republic]. Vol. 3. – Academia, Praha.
Slavík B., Chrtek J. jun. & Štěpánková J. (eds) (2000) Květena České republiky [Flora of the Czech Republic]. Vol. 6. – Academia, Praha.
Slavík B., Chrtek J. jun. & Tomšovic P. (eds) (1997) Květena České republiky [Flora of the Czech Republic]. Vol. 5. – Academia, Praha.
Slavík B., Smejkal M., Dvořáková M. & Grulich V. (eds) (1995) Květena České republiky [Flora of the Czech Republic]. Vol. 4. – Academia, Praha.
Slavík B., Štěpánková J. & Štěpánek J. (eds) (2004) Květena České republiky [Flora of the Czech Republic]. Vol. 7. – Academia, Praha.
Štěpánková J., Chrtek J. jun. & Kaplan Z. (eds) (2010) Květena České republiky [Flora of the Czech Republic]. Vol. 8. – Academia, Praha.
Wu Z., Raven P. H. & Huang D. (eds) (1994) Flora of China. – Science Press, Beijing & Missouri Botanical
Garden, St. Louis.
Inflorescence types follow the morphological system used in the Flora of the Czech Republic (vols. 1–8; Hejný et al. 1988–1992, Slavík et al. 1997–2004, Štěpánková et al. 2010). As the Czech terminology used for inflorescences does not match the English terminology, we use Latin terms in the English version of the Pladias Database. The exact identification of the inflorescence type is often equivocal because of varying interpretations of the same object. In species with unisexual flowers, male and female flowers can occur in different inflorescence types. In other cases, it is not possible to identify the inflorescence without detailed knowledge of evolutionary morphology, e.g. umbella vs pseudumbella in the genus Butomus. There are also compound inflorescences, in some cases with very different structure of their parts, especially in Asteraceae, which can have even triple inflorescences (e.g. Echinops sphaerocephalus often has an anthella ex capitulis anthodiorum composita).
The information was extracted mainly from the descriptions in the Flora of the Czech Republic (vols. 1–8; Hejný et al. 1988–1992, Slavík et al. 1997–2004, Štěpánková et al. 2010). For the taxa not treated in that flora or if some uncertainties occurred, mainly concerning some alien taxa, information was taken from the descriptions in the Flora of North America (Flora of North America Editorial Committee 1993), the Flora of China (Wu et al. 1994) and the Flora of Pakistan (www.tropicos.org/Project/Pakistan). In critical groups (e.g. Rubus), especially in recently described species, inflorescence type was taken from the original descriptions.
Grulich V. & Štěpánková P. (2019) Inflorescence type. – www.pladias.cz.
Flora of North America Editorial Committee (eds) (1993) Flora of North America North of Mexico. – Oxford
University Press, New York.
Flora of Pakistan. – http://www.tropicos.org/Project/Pakistan
Hejný S., Slavík B., Chrtek J., Tomšovic P. & Kovanda M. (eds) (1988) Květena České socialistické republiky [Flora of the Czech Socialist Republic]. Vol. 1. – Academia, Praha.
Hejný S., Slavík B., Hrouda L. & Skalický V. (eds) (1990) Květena České republiky [Flora of the Czech Republic]. Vol. 2. – Academia, Praha.
Hejný S., Slavík B., Kirschner J. & Křísa B. (eds) (1992) Květena České republiky [Flora of the Czech Republic]. Vol. 3. – Academia, Praha.
Slavík B., Chrtek J. jun. & Štěpánková J. (eds) (2000) Květena České republiky [Flora of the Czech Republic]. Vol. 6. – Academia, Praha.
Slavík B., Chrtek J. jun. & Tomšovic P. (eds) (1997) Květena České republiky [Flora of the Czech Republic]. Vol. 5. – Academia, Praha.
Slavík B., Smejkal M., Dvořáková M. & Grulich V. (eds) (1995) Květena České republiky [Flora of the Czech Republic]. Vol. 4. – Academia, Praha.
Slavík B., Štěpánková J. & Štěpánek J. (eds) (2004) Květena České republiky [Flora of the Czech Republic]. Vol. 7. – Academia, Praha.
Štěpánková J., Chrtek J. jun. & Kaplan Z. (eds) (2010) Květena České republiky [Flora of the Czech Republic]. Vol. 8. – Academia, Praha.
Wu Z., Raven P. H. & Huang D. (eds) (1994) Flora of China. – Science Press, Beijing & Missouri Botanical
Garden, St. Louis.
Plant parasitism is based on either of two mechanisms. The first group of parasitic plants involves those parasitizing directly on another plant. These plants are called haustorial parasites. They take resources from the host’s vascular bundles using a specialized organ, the haustorium. The second group comprises mycoheterotrophic plants, which parasitize fungi via mycorrhizal interaction and gain organic carbon from them.
Plants in both groups display variable dependence on their host organism. The haustorial parasites include two distinct functional groups: green hemiparasites and holoparasites. Green hemiparasites are partial parasites that retain photosynthetic ability but obtain all mineral resources and a part of the organic carbon from the host. Holoparasites are non-green full parasites unable to photosynthesize. Location of the haustorial attachment to the host (root or stem) is another essential functional trait. The distinction between partial and full parasitism in haustorial parasites may not be straightforward. In the Czech flora, it is nevertheless possible to distinguish between stem hemi- and holoparasites, which are difficult to separate on the global scale (Těšitel 2016). Consequently, we use a traditional classification here and classify as holoparasites those plants that are in adulthood mostly without chlorophyll, even though some of them might have some chlorophyll and perform residual photosynthesis (e.g. Cuscuta).
In mycoheterotrophic plants, there is a continuum from initial mycoheterotrophs through partial mycoheterotrophs to full mycoheterotrophs. In the initial mycoheterotrophs, only initial stages, i.e. gametophytes or seedlings, are dependent on the fungus, whereas adult plants are autotrophic, while still depending on mycorrhizal symbiosis as a source of water and mineral nutrients. In the partial mycoheterotrophs, photosynthesizing adults obtain from their mycorrhizal fungi not only water and mineral nutrients but also different amounts of organic carbon. The full mycoheterotrophs lost their chlorophyll and are thus fully parasitic. In some partial mycoheterotrophs (e.g. the genus Cephalanthera), chlorotic individuals can be found, which lack chlorophyll and fully depend on their hosts.
Classification of haustorial parasites follows Těšitel (2016) with a further distinction of stem hemi- and holoparasites, and identification of mycoheterotrophs follows Merckx (2012).
Těšitel J., Těšitelová T., Blažek P. & Lepš J. (2016) Parasitism and mycoheterotrophy. – www.pladias.cz.
Těšitel J. (2016) Functional biology of parasitic plants: a review. – Plant Ecology and Evolution 149: 5–20.
Merckx V. S. F. T. (2012) Mycoheterotrophy: the biology of plants living on fungi. – Springer, Berlin.
Carnivorous plants attract, trap and kill their prey, animals (mainly insects and small crustaceans) and protozoans, and subsequently absorb the nutrients from their dead bodies.
Hejný S., Slavík B., Chrtek J., Tomšovic P. & Kovanda M. (eds) (1988) Květena České socialistické republiky [Flora of the Czech Socialist Republic]. Vol. 1. – Academia, Praha.
Hejný S., Slavík B., Hrouda L. & Skalický V. (eds) (1990) Květena České republiky [Flora of the Czech Republic]. Vol. 2. – Academia, Praha.
Hejný S., Slavík B., Kirschner J. & Křísa B. (eds) (1992) Květena České republiky [Flora of the Czech Republic]. Vol. 3. – Academia, Praha.
Slavík B., Chrtek J. jun. & Štěpánková J. (eds) (2000) Květena České republiky [Flora of the Czech Republic]. Vol. 6. – Academia, Praha.
Slavík B., Chrtek J. jun. & Tomšovic P. (eds) (1997) Květena České republiky [Flora of the Czech Republic]. Vol. 5. – Academia, Praha.
Slavík B., Smejkal M., Dvořáková M. & Grulich V. (eds) (1995) Květena České republiky [Flora of the Czech Republic]. Vol. 4. – Academia, Praha.
Slavík B., Štěpánková J. & Štěpánek J. (eds) (2004) Květena České republiky [Flora of the Czech Republic]. Vol. 7. – Academia, Praha.
Štěpánková J., Chrtek J. jun. & Kaplan Z. (eds) (2010) Květena České republiky [Flora of the Czech Republic]. Vol. 8. – Academia, Praha.
Chromosome number is the somatic number of chromosomes in the zygotic stage, i.e. without possible endopolyploidy of somatic tissues. If different chromosome numbers are known for a taxon, the database contains primarily the number reported from the Czech Republic or the number that is the most common in this country or can be expected to be the most common based on the data from neighbouring countries. Other existing and less common chromosome numbers are reported in brackets. The survey does not take into account odd chromosome numbers of individual, aneuploid, euploid, haploid or autopolyploid plants, which may rarely originate in natural or experimental populations. It also disregards the numbers reported in early studies or from geographically distant areas for which the taxonomic identity with Czech plants is unclear.
The data compilation is based mainly on the Flora of the Czech Republic (vols. 1–8; Hejný et al. 1988–1992, Slavík et al. 1997–2004, Štěpánková et al. 2010) and the Chromosome Count Database (Rice et al. 2015; http://ccdb.tau.ac.il/). If only information about ploidy level is available from flow cytometry measurements, but no chromosome number is known, the number typical of the given ploidy in closely related taxa is indicated.
Šmarda P. (2018) Chromosome number (2n). – www.pladias.cz.
Hejný S., Slavík B., Chrtek J., Tomšovic P. & Kovanda M. (eds) (1988) Květena České socialistické republiky [Flora of the Czech Socialist Republic]. Vol. 1. – Academia, Praha.
Hejný S., Slavík B., Hrouda L. & Skalický V. (eds) (1990) Květena České republiky [Flora of the Czech Republic]. Vol. 2. – Academia, Praha.
Hejný S., Slavík B., Kirschner J. & Křísa B. (eds) (1992) Květena České republiky [Flora of the Czech Republic]. Vol. 3. – Academia, Praha.
Rice A., Glick L., Abadi S., Einhorn M., Kopelman N. M., Salman-Minkov A., Mayzel J., Chay O. & Mayrose I. (2015) The chromosome counts database (CCDB): a community resource of plant chromosome numbers. – New Phytologist 206: 19–26.
Slavík B., Chrtek J. jun. & Štěpánková J. (eds) (2000) Květena České republiky [Flora of the Czech Republic]. Vol. 6. – Academia, Praha.
Slavík B., Chrtek J. jun. & Tomšovic P. (eds) (1997) Květena České republiky [Flora of the Czech Republic]. Vol. 5. – Academia, Praha.
Slavík B., Smejkal M., Dvořáková M. & Grulich V. (eds) (1995) Květena České republiky [Flora of the Czech Republic]. Vol. 4. – Academia, Praha.
Slavík B., Štěpánková J. & Štěpánek J. (eds) (2004) Květena České republiky [Flora of the Czech Republic]. Vol. 7. – Academia, Praha.
Štěpánková J., Chrtek J. jun. & Kaplan Z. (eds) (2010) Květena České republiky [Flora of the Czech Republic]. Vol. 8. – Academia, Praha.
Ploidy level is the number of somatic chromosomal sets in the zygotic stage, i.e. without the possible endopolyploidy of somatic tissues. Ploidy level determines the minimum copy number of most genes, influences minimal cell size and other morphological and ecological properties of the taxon (Stebbins 1950, Levin 2002, Tate et al. 2005). The data presented here are based on the traits Chromosome number and 2C genome size, and to a lesser extent also on a literature search of flow cytometry studies related to the area of the Czech Republic. The reported values are especially those reported from the Czech Republic or those ploidy levels that are most frequent in this country or at least are assumed to be the most frequent based on the data from neighbouring countries. The other existing (minor) ploidy levels (cytotypes) that are documented from the Czech Republic or that may be expected to occur here based on the records from neighbouring countries are indicated in brackets. The survey does not take into account the observations of individual haploid or autopolyploid plants which may rarely originate in natural or experimental populations. It also disregards the ploidy levels derived from the numbers of chromosomes reported in early studies or from geographically distant areas, where taxonomic identity with Czech plants is uncertain.
The size of one chromosomal set (x) or the “base chromosome number” for calculating the ploidy level is derived here from the lowest chromosome number known in the given genus or the group of closely related genera (e.g. Raven 1975). This minimum chromosome number is generally considered to correspond to diploids (i.e., two chromosomal sets). A taxon is considered as polyploid whenever its chromosome number and genome size are jointly ± doubled (or otherwise multiplied) compared to the diploid taxa of related genera. It may therefore sometimes happen that no diploid taxa are known in some genera. The absence of diploids in a given genus may result from (i) the lack of karyological data, (ii) the extinction of the diploid relative(s), or (iii) a polyploidy event that predated the origin of the whole genus, with the current genomes still showing little signs of backward “diploidization”. The joint usage of the chromosome number and genome size enables estimation of ploidy levels also for the taxa with holocentric chromosomes (Cyperaceae, Drosera, Juncaceae, Cuscuta sect. Cuscuta and C. sect. Gramica). In these taxa, the chromosome number does not need to be positively correlated with the ploidy level due to possible chromosomal fissions and fusions (agmatoploidy and symploidy, respectively; Bureš et al. 2013). To handle the chromosomal fusions in Luzula, chromosome size categories as defined by Nordeskiöld (1951) were further considered to estimate the actual ploidy level. Ploidy level estimates in highly polyploid genomes of Viola follow Marcussen et al. (2015).
Šmarda P. (2018) Ploidy level (x). – www.pladias.cz.
Bureš P., Zedek F. & Marková M. (2013) Holocentric chromosomes. – In: Leitch I. J., Greilhuber J., Wendel J. & Wendel J. (eds), Plant genome diversity. Vol. 2. Physical structure, behaviour and evolution of plant genomes, p. 187–208, Springer, Wien.
Dar T.-U.-H. & Rehman R.-U. (2017) Polyploidy: recent trends and future perspectives. – Springer, New Delhi.
Levin D. A. (2002) The role of chromosomal change in plant evolution. – Oxford University Press, Oxford.
Nordenskiöld H. (1951) Cytotaxonomical studies in the genus Luzula. – Hereditas 37: 325–355.
Raven P. H. (1975) The bases of angiosperm phylogeny: cytology. – Annals of the Missouri Botanical Garden
62: 724–764.
Stebbins G. L. (1950) Variation and evolution in plants. – Columbia University Press, New York.
Tate J. A., Soltis D. E. & Soltis P. S. (2005) Polyploidy in plants. – In: Gregory R. T. (ed.), The evolution of the
genome, p. 371–426, Elsevier, Amsterdam.
2C genome size is the somatic nuclear DNA content in a zygotic cell measured in megabase pairs (Mbp). This measure can vary among taxa due to both polyploidy and the variability in the content of non-coding DNA (Leitch & Greilhuber 2013). Genome size influences minimum cell size, duration of the cell cycle and cell division, and nutrient requirements. Therefore, it may have a considerable influence on ecological strategies of plants (Bennett 1987, Veselý et al. 2012, Greilhuber & Leitch 2013). Most values were measured in plants collected in the Czech Republic (Šmarda et al. 2019). The data always refer to the dominant chromosome number and the dominant ploidy level of the given taxon.
Šmarda P., Knápek O., Březinová A., Horová L., Grulich V., Danihelka J., Veselý P., Šmerda J., Rotreklová O. & Bureš P. (2019) Genome sizes and genomic guanine+cytosine (GC) contents of the Czech vascular flora with new estimates for 1700 species. – Preslia 91: 117–142.
Bennett M. D. (1987) Variation in genomic form in plants and its ecological implications. – New Phytologist 106 (Suppl.): 177–200.
Greilhuber J. & Leitch I. J. (2013) Genome size and the phenotype. – In: Leitch I. J., Greilhuber J., Doležel J. & Wendel J. (eds), Plant genome diversity. Vol. 2. Physical structure, behaviour and evolution of plant genomes, p. 323–344, Springer, Wien.
Leitch I. J. & Greilhuber J. (2013) Genome size diversity and evolution in land plants. – In: Leitch I. J., Greilhuber J., Doležel J. & Wendel J. (eds), Plant genome diversity. Vol. 2. Physical structure, behaviour and evolution of plant genomes, p. 307–322, Springer, Wien.
Veselý P., Bureš P., Šmarda P. & Pavlíček T. (2012) Genome size and DNA base composition of geophytes: the mirror of phenology and ecology? – Annals of Botany 109: 65–75.
1Cx monoploid genome size is the amount of DNA contained in one set of chromosomes measured in megabase pairs (Mbp). The values were obtained for each taxon by dividing its 2C genome size by the respective ploidy level (Greilhuber et al. 2005). Differences in 1Cx values among taxa are therefore virtually free of the polyploidy effect (i.e. only due to amplification of non-coding DNA). However, the 1Cx values in polyploids are usually slightly smaller due to the increased tendency to eliminate the duplicated, redundant DNA (Leitch & Bennett 2004). Because the 1Cx values tend to be similar in related taxa, they can be used to roughly estimate the 2C genome size in related taxa for which only the ploidy level is known so far. Conversely, they can be used to estimate the ploidy levels based on the known 2C genome size. The data were taken from Šmarda et al. (2019).
Šmarda P., Knápek O., Březinová A., Horová L., Grulich V., Danihelka J., Veselý P., Šmerda J., Rotreklová O. & Bureš P. (2019) Genome sizes and genomic guanine+cytosine (GC) contents of the Czech vascular flora with new estimates for 1700 species. – Preslia 91: 117–142.
Greilhuber J., Doležel J., Lysák M. A. & Bennett M. D. (2005) The origin, evolution and proposed stabilization of the terms ‘genome size’ and ‘C-value’ to describe nuclear DNA content. – Annals of Botany 95: 255–260.
Leitch I. J. & Bennett M. D. (2004) Genome downsizing in polyploid plants. – Biological Journal of the Linnean Society 82: 651–663.
Genomic GC content is the percentage of guanine and cytosine bases in nuclear DNA. It influences the thermal stability of DNA, packing of condensed DNA within the nucleus, the energetic cost of DNA synthesis or cell sensitivity to desiccation (Šmarda & Bureš 2012, Šmarda et al. 2014). For the vast majority of taxa, these data were measured in plants collected in the Czech Republic (Šmarda et al. 2019). The data always refer to the dominant chromosome number and dominant ploidy of the given taxon. Differences up to 1% in closely related taxa or up to 2% in unrelated taxa may be considered insignificant because of possible method errors (Šmarda et al. 2012).
Šmarda P., Knápek O., Březinová A., Horová L., Grulich V., Danihelka J., Veselý P., Šmerda J., Rotreklová O. & Bureš P. (2019) Genome sizes and genomic guanine+cytosine (GC) contents of the Czech vascular flora with new estimates for 1700 species. – Preslia 91: 117–142.
Šmarda P. & Bureš P. (2012) The variation of base composition in plant genomes. – In: Wendel J., Greilhuber J., Doležel J. & Leitch I. J. (eds), Plant genome diversity. Vol. 1. Plant genomes, their residents, and their evolutionary dynamics, p. 209–235, Springer, Heidelberg.
Šmarda P., Bureš P., Šmerda J. & Horová L. (2012) Measurements of genomic GC content in plant genomes with flow cytometry: a test for reliability. – New Phytologist 193: 513–521.
Šmarda P., Bureš P., Horová L., Leitch I. J., Mucina L., Pacini E., Tichý L., Grulich V. & Rotreklová O. (2014) Ecological and evolutionary significance of genomic GC content diversity in monocots. – Proceedings of the National Academy of Sciences of the USA 111: E4096–E4102.
Taxa are classified according to whether they are native or alien to the Czech Republic. Following the definitions used in invasion ecology, native taxa are those that have evolved in the area of the Czech Republic or immigrated there without human assistance from the area where they had evolved. Alien taxa are those whose presence is a result of intentional or unintentional introduction by human activity and can be divided based on their residence time. The alien taxa are divided based on their residence time into archaeophytes and neophytes. Archaeophytes are taxa occurring in the wild that were introduced between the beginning of Neolithic agriculture and the year 1500, i.e. the beginning of intercontinental overseas trade after the discovery of the Americas. Neophytes are taxa occurring in the wild that were introduced after 1500 (see Richardson et al. 2000 for detailed definitions). Some taxa introduced in the Late Middle Ages or Early Modern Period, but with no exact information on the introduction date, were assigned to a joint category of Archaeophyte/neophyte. Additionally, some frequently cultivated taxa that are not known to have escaped from cultivation are listed as a separate category Cultivated. Category Lack of evidence of occurrence in the wild includes taxa for which spontaneous occurrence in the wild is doubtful. Taxa assigned to the category Absent in Czechia are not sufficiently supported by reliable records or occurred just once and disappeared.
The data included in the database follow the third edition of the Catalogue of alien plants of the Czech Republic (Pyšek et al. 2022 and references related to individual taxa therein).
Pyšek P., Sádlo J., Chrtek J. Jr., Chytrý M., Kaplan Z., Pergl J., Pokorná A., Axmanová I., Čuda J., Doležal J., Dřevojan P., Hejda M., Kočár P., Kortz A., Lososová Z., Lustyk P., Skálová H., Štajerová K., Večeřa M., Vítková M., Wild J. & Danihelka J. (2022) Catalogue of alien plants of the Czech Republic (3rd edition): species richness, status, distributions, habitats, regional invasion levels, introduction pathways and impacts. – Preslia 94: 447–577.
Richardson D. M., Pyšek P., Rejmánek M., Barbour M. G., Panetta F. D. & West C. J. (2000) Naturalization and invasion of alien plants: concepts and definitions. – Diversity and Distributions 6: 93–107.
Invasion status is a classification of alien taxa into three categories reflecting their position in the invasion process. Alien taxa that only occasionally reproduce in the wild in the Czech Republic, do not form self-replacing populations, and rely on repeated introductions for their persistence are termed casual. Naturalized taxa are alien plants that reproduce in the wild and sustain populations over many life cycles without direct intervention by humans (or despite human intervention). Invasive plants are naturalized plants that produce reproductive offspring, often in large numbers, at considerable distances from parent plants and thus have the potential to spread over an extensive area (Richardson et al. 2000, 2011). This classification does not apply to native taxa, which are reported as separate categories. The data were taken from the third edition of the Catalogue of alien plants of the Czech Republic (Pyšek et al. 2022 and references related to individual taxa therein).
Pyšek P., Sádlo J., Chrtek J. Jr., Chytrý M., Kaplan Z., Pergl J., Pokorná A., Axmanová I., Čuda J., Doležal J., Dřevojan P., Hejda M., Kočár P., Kortz A., Lososová Z., Lustyk P., Skálová H., Štajerová K., Večeřa M., Vítková M., Wild J. & Danihelka J. (2022) Catalogue of alien plants of the Czech Republic (3rd edition): species richness, status, distributions, habitats, regional invasion levels, introduction pathways and impacts. – Preslia 94: 447–577.
Richardson D. M., Pyšek P. & Carlton J. T. (2011) A compendium of essential concepts and terminology in biological invasions. – In: Richardson D. M. (ed.), Fifty years of invasion ecology: the legacy of Charles Elton, p. 409–420, Blackwell Publishing, Oxford.
Richardson D. M., Pyšek P., Rejmánek M., Barbour M. G., Panetta F. D. & West C. J. (2000) Naturalization and invasion of alien plants: concepts and definitions. – Diversity and Distributions 6: 93–107.
This information is given for alien taxa only. These taxa are classified according to their geographic origin (native range) at the level of continents; those with a native range encompassing more than one continent are assigned to two or more categories. Origin in Europe refers to the non-Mediterranean parts of this continent other than the Czech Republic. The Mediterranean region comprises parts of southern Europe, northern Africa and western Asia from Turkey and Israel to Afghanistan, which are characterized by the Mediterranean-type climate and the occurrence of sclerophyllous evergreen vegetation. Conversely, records of origin in Africa, Asia and Europe do not relate to the Mediterranean part of these continents. Hybrids and species that originated through recent hybridization are listed as a separate category. Anecophytes are taxa for which native range is unknown or highly uncertain. The data were taken from the third edition of the Catalogue of alien plants of the Czech Republic (Pyšek et al. 2022 and references related to individual taxa therein).
Pyšek P., Sádlo J., Chrtek J. Jr., Chytrý M., Kaplan Z., Pergl J., Pokorná A., Axmanová I., Čuda J., Doležal J., Dřevojan P., Hejda M., Kočár P., Kortz A., Lososová Z., Lustyk P., Skálová H., Štajerová K., Večeřa M., Vítková M., Wild J. & Danihelka J. (2022) Catalogue of alien plants of the Czech Republic (3rd edition): species richness, status, distributions, habitats, regional invasion levels, introduction pathways and impacts. – Preslia 94: 447–577.
The year of the first reported occurrence in the wild in the Czech Republic is given for neophytes. Data were extracted from the third edition of the Catalogue of alien plants of the Czech Republic (Pyšek et al. 2022); however, for many species, this information is not available.
Pyšek P., Sádlo J., Chrtek J. Jr., Chytrý M., Kaplan Z., Pergl J., Pokorná A., Axmanová I., Čuda J., Doležal J., Dřevojan P., Hejda M., Kočár P., Kortz A., Lososová Z., Lustyk P., Skálová H., Štajerová K., Večeřa M., Vítková M., Wild J. & Danihelka J. (2022) Catalogue of alien plants of the Czech Republic (3rd edition): species richness, status, distributions, habitats, regional invasion levels, introduction pathways and impacts. – Preslia 94: 447–577.
Period of introduction is divided into categories from the Neolithic to the present time. The assessment is based on archaeobotanical and also floristic data where applicable. For taxa without precise dating, only merged categories of longer time periods are provided.
Data were extracted from the third edition of the Catalogue of alien plants of the Czech Republic (Pyšek et al. 2022).
Pyšek P., Sádlo J., Chrtek J. Jr., Chytrý M., Kaplan Z., Pergl J., Pokorná A., Axmanová I., Čuda J., Doležal J., Dřevojan P., Hejda M., Kočár P., Kortz A., Lososová Z., Lustyk P., Skálová H., Štajerová K., Večeřa M., Vítková M., Wild J. & Danihelka J. (2022) Catalogue of alien plants of the Czech Republic (3rd edition): species richness, status, distributions, habitats, regional invasion levels, introduction pathways and impacts. – Preslia 94: 447–577.
This information is available for alien taxa only. Taxa are classified according to the mode of introduction, with the distinction made between an intentional (deliberate) and unintentional (accidental) pathway (Hulme et al. 2008). A taxon can be assigned to more than one introduction pathway. The pathway classification and data for individual taxa follow the third edition of the Catalogue of alien plants of the Czech Republic (Pyšek et al. 2022).
The classification includes the following introduction pathways:
Intentional introduction: 1 ornamental – cultivation for ornamental purposes in a garden or public green space; 2 collection – cultivation for scientific or collection purposes in a garden or park; 3 nature – ornamental planting in natural habitats, including deceptive enrichment of regional flora or inclusion of alien plants in seed mixtures sold as “wild meadows”; 4 crops – cultivation of crops such as fruits, vegetables, cereals, spices; 5 forest – forestry and wildlife management, e.g. planting trees in forestry plantations or cultivation of crops in forests as a fodder for game; 6 landscaping, e.g. afforestation, land reclamation, roadside tree belts, tree alleys; 7 other – cultivation for other purposes, e.g. forage crops, plants for basketry, beekeeping and pharmacy.
Unintentional introduction: 8 agriculture – introduction associated with agriculture: weeds in fields (e.g. cereals, flax), vegetable beds and vineyards; 9 plantation – introduction associated with fodder crop cultivation, sowing meadows and planting forest trees; 10 horticulture – introduction associated with the horticultural sale of ornamental plants, i.e. weeds of ornamental gardens; 11 traffic – dispersal by vehicles, trains, shipping, urban tourism; 12 industry – dispersal through mining or production/distribution of commodities, e.g. ores, wool; 13 humans – other unintended vectors associated with anthropogenic habitats; 14 nature – other unintended vectors associated with natural habitats, e.g. dispersal by wind, water, animals.
Pyšek P., Sádlo J., Chrtek J. Jr., Chytrý M., Kaplan Z., Pergl J., Pokorná A., Axmanová I., Čuda J., Doležal J., Dřevojan P., Hejda M., Kočár P., Kortz A., Lososová Z., Lustyk P., Skálová H., Štajerová K., Večeřa M., Vítková M., Wild J. & Danihelka J. (2022) Catalogue of alien plants of the Czech Republic (3rd edition): species richness, status, distributions, habitats, regional invasion levels, introduction pathways and impacts. – Preslia 94: 447–577.
Hulme P. E., Bacher S., Kenis M., Klotz S., Kühn I., Minchin D., Nentwig W., Olenin S., Panov V., Pergl J., Pyšek P., Roques A., Sol D., Solarz W. & Vilà M. (2008) Grasping at the routes of biological invasions: a framework for integrating pathways into policy. – Journal of Applied Ecology 45: 403–414.
National Red List categories were taken from the 2017 edition of the Red List of Vascular Plants of the Czech Republic (Grulich 2017). These categories, introduced in the previous editions of the Czech Red List, are different from the IUCN Red List categories. The main category “A” includes extinct or missing taxa, while the main category “C” includes endangered, near threatened and data deficient taxa.
Grulich V. (2017) Červený seznam cévnatých rostlin ČR [The Red List of vascular plants of the Czech Republic]. – Příroda 35: 75–132.
International Red List categories defined by the IUCN were taken from the 2017 edition of the Red List of Vascular Plants of the Czech Republic (Grulich 2017). Taxon assignments to these categories follow the internationally accepted rules (IUCN 2012, 2014). To some extent, the definitions of these categories differ from the national categories used in the previous Czech Red Lists. The national Red List included only threatened or possibly threatened taxa, implying that the non-included taxa are not threatened. Therefore, the non-included taxa are classified here as LC(NA) – least concern (taxon is not on the Red List).
Grulich V. (2017) Červený seznam cévnatých rostlin ČR [The Red List of vascular plants of the Czech Republic]. – Příroda 35: 75–132.
IUCN (2012) Guidelines for application of IUCN Red List criteria at regional and national levels. Version 4.0. – IUCN, Gland.
IUCN (2014) Guidelines for using the IUCN Red List categories and criteria. Version 11. – IUCN, Gland.
Legal protection in the Czech Republic concerns the specifically protected species, i.e. rare taxa, threatened taxa and taxa significant from a cultural or scientific point of view that are listed in Annex II of the Decree of the Ministry of the Environment no. 395/1992. They comprise 487 taxa of vascular plants divided into three categories according to their vulnerability: critically threatened, endangered and vulnerable.
Decree no. 395/1992 of the Ministry of the Environment of the Czech Republic.