Plant heights are relevant for the Czech Republic. They are measured in metres and relate to fully developed mature generative plants growing in the wild. Each taxon is characterized by two values: minimum (lower limit of the common range) and maximum (upper limit of the common range). The data were taken from the Key to the Flora of the Czech Republic (Kaplan et al. 2019).
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.
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.
Grime (1974, 1979) distinguished three basic ecological strategies of plants: (i) competitive strategy (C), advantageous in stable habitats where resources are abundant, conditions not extreme and the disturbance level low; (ii) stress-tolerant strategy (S), advantageous where resources are scarce, conditions severe and highly variable, but disturbance is uncommon; and (iii) ruderal strategy (R), advantageous where resources are abundant and conditions not extreme, but the disturbance frequency is high.
Taxa of the Czech flora were assigned to life strategies based on the method proposed by Pierce et al. (2017). The life strategies calculated using this method represent the trade-off in resource investment between three key leaf traits: leaf area (LA; high in competitive taxa), leaf dry matter content (LDMC; high in stress-tolerant taxa) and specific leaf area (SLA; high in ruderal taxa). Scores that express the degree of C-, S- and R-selection are calculated from these traits. These scores are expressed on a percentage scale, and the sum of the three scores for individual taxa is 100%. Based on these scores, the taxa are assigned to the basic primary strategies C, S and R, intermediate strategies CS, CR, SR and CSR, and transitions between them, e.g. C/CS or SR/CSR (sensu Grime 1979). The data on leaf traits for these calculations or calculated values were taken from the LEDA database (Kleyer et al. 2008) and some other sources (Bjorkman et al. 2018, Dayrell et al. 2018, Findurová 2018, Tavşanoğlu & Pausas 2018, Wang et al. 2018, Guo et al. 2019). The Pladias database contains both the score values for the three categories C, S, R and the categorized life strategies.
Guo W.-Y. & Pierce S. (2019) Life strategy. – www.pladias.cz.
Bjorkman A. D., Myers-Smith I. H., Elmendorf S. C. et al. (2018) Tundra Trait Team: A database of plant traits spanning the tundra biome. – Global Ecology and Biogeography 27: 1402–1411.
Dayrell R. L., Arruda A. J., Pierce S., Negreiros D., Meyer P. B., Lambers H. & Silveira F. A. (2018)
Ontogenetic shifts in plant ecological strategies. – Functional Ecology 32: 2730–2741.
Findurová A. (2018) Variabilita listových znaků SLA a LDMC vybraných druhů rostlin České republiky [Variability
of leaf traits SLA and LDMC in selected species of the Czech flora]. – Master thesis, Masaryk University, Brno.
Grime J. P. (1974) Vegetation classification by reference to strategies. – Nature 250: 26–31.
Grime J. P. (1979) Plant strategies and vegetation processes. – Wiley, Chichester.
Kleyer M., Bekker R. M., Knevel I. C., Bakker J. P., Thompson K., Sonnenschein M., Poschlod P., van
Groenendael J. M., Klimeš L., Klimešová J., Klotz S., Rusch G. M., Hermy M., Adriaens D., Boedeltje G.,
Bossuyt B., Dannemann A., Endels P., Götzenberger L., Hodgson J. G., Jackel A. K., Kühn I., Kunzmann D.,
OzingaW. A., Romermann C., Stadler M., Schlegelmilch J., Steendam H. J., Tackenberg O., Wilmann B.,
Cornelissen J. H. C., Eriksson O., Garnier E. & Peco B. (2008) The LEDA Traitbase: a database of life-history
traits of the Northwest European flora. – Journal of Ecology 96: 1266–1274.
Pierce S., Negreiros D., Cerabolini B. E. L., Kattge J., Díaz S., Kleyer M., Shipley B., Wright S. J.,
Soudzilovskaia N. A., Onipchenko V. G., van Bodegom P. M., Frenette-Dussault C., Weiher E., Pinho B. X.,
Cornelissen J. H. C., Grime J. P., Thompson K., Hunt R., Wilson P. J., Buffa G., Nyakunga O. C., Reich P. B.,
CaccianigaM., Mangili F., Ceriani R. M., Luzzaro A., Brusa G., Siefert A., Barbosa N. P. U., Chapin F. S.,
Cornwell W. K., Fang J., Fernandes G. W., Garnier E., Le Stradic S., Peńuelas J., Melo F. P. L., Slaviero A.,
Tabarelli M. & Tampucci D. (2017) A global method for calculating plant CSR ecological strategies
applied across biomes world-wide. – Functional Ecology 31: 444–457.
Tavşanoğlu Ç. & Pausas J. G. (2018) A functional trait database for Mediterranean Basin plants. – Scientific
Data 5: 180135.
Grime (1974, 1979) distinguished three basic ecological strategies of plants: (i) competitive strategy (C), advantageous in stable habitats where resources are abundant, conditions not extreme and the disturbance level low; (ii) stress-tolerant strategy (S), advantageous where resources are scarce, conditions severe and highly variable, but disturbance is uncommon; and (iii) ruderal strategy (R), advantageous where resources are abundant and conditions not extreme, but the disturbance frequency is high.
Taxa of the Czech flora were assigned to life strategies based on the method proposed by Pierce et al. (2017). The life strategies calculated using this method represent the trade-off in resource investment between three key leaf traits: leaf area (LA; high in competitive taxa), leaf dry matter content (LDMC; high in stress-tolerant taxa) and specific leaf area (SLA; high in ruderal taxa). Scores that express the degree of C-, S- and R-selection are calculated from these traits. These scores are expressed on a percentage scale, and the sum of the three scores for individual taxa is 100%. Based on these scores, the taxa are assigned to the basic primary strategies C, S and R, intermediate strategies CS, CR, SR and CSR, and transitions between them, e.g. C/CS or SR/CSR (sensu Grime 1979). The data on leaf traits for these calculations or calculated values were taken from the LEDA database (Kleyer et al. 2008) and some other sources (Bjorkman et al. 2018, Dayrell et al. 2018, Findurová 2018, Tavşanoğlu & Pausas 2018, Wang et al. 2018, Guo et al. 2019). The Pladias database contains both the score values for the three categories C, S, R and the categorized life strategies.
Guo W.-Y. & Pierce S. (2019) Life strategy. – www.pladias.cz.
Bjorkman A. D., Myers-Smith I. H., Elmendorf S. C. et al. (2018) Tundra Trait Team: A database of plant traits spanning the tundra biome. – Global Ecology and Biogeography 27: 1402–1411.
Dayrell R. L., Arruda A. J., Pierce S., Negreiros D., Meyer P. B., Lambers H. & Silveira F. A. (2018)
Ontogenetic shifts in plant ecological strategies. – Functional Ecology 32: 2730–2741.
Findurová A. (2018) Variabilita listových znaků SLA a LDMC vybraných druhů rostlin České republiky [Variability
of leaf traits SLA and LDMC in selected species of the Czech flora]. – Master thesis, Masaryk University, Brno.
Grime J. P. (1974) Vegetation classification by reference to strategies. – Nature 250: 26–31.
Grime J. P. (1979) Plant strategies and vegetation processes. – Wiley, Chichester.
Kleyer M., Bekker R. M., Knevel I. C., Bakker J. P., Thompson K., Sonnenschein M., Poschlod P., van
Groenendael J. M., Klimeš L., Klimešová J., Klotz S., Rusch G. M., Hermy M., Adriaens D., Boedeltje G.,
Bossuyt B., Dannemann A., Endels P., Götzenberger L., Hodgson J. G., Jackel A. K., Kühn I., Kunzmann D.,
OzingaW. A., Romermann C., Stadler M., Schlegelmilch J., Steendam H. J., Tackenberg O., Wilmann B.,
Cornelissen J. H. C., Eriksson O., Garnier E. & Peco B. (2008) The LEDA Traitbase: a database of life-history
traits of the Northwest European flora. – Journal of Ecology 96: 1266–1274.
Pierce S., Negreiros D., Cerabolini B. E. L., Kattge J., Díaz S., Kleyer M., Shipley B., Wright S. J.,
Soudzilovskaia N. A., Onipchenko V. G., van Bodegom P. M., Frenette-Dussault C., Weiher E., Pinho B. X.,
Cornelissen J. H. C., Grime J. P., Thompson K., Hunt R., Wilson P. J., Buffa G., Nyakunga O. C., Reich P. B.,
CaccianigaM., Mangili F., Ceriani R. M., Luzzaro A., Brusa G., Siefert A., Barbosa N. P. U., Chapin F. S.,
Cornwell W. K., Fang J., Fernandes G. W., Garnier E., Le Stradic S., Peńuelas J., Melo F. P. L., Slaviero A.,
Tabarelli M. & Tampucci D. (2017) A global method for calculating plant CSR ecological strategies
applied across biomes world-wide. – Functional Ecology 31: 444–457.
Tavşanoğlu Ç. & Pausas J. G. (2018) A functional trait database for Mediterranean Basin plants. – Scientific
Data 5: 180135.
Grime (1974, 1979) distinguished three basic ecological strategies of plants: (i) competitive strategy (C), advantageous in stable habitats where resources are abundant, conditions not extreme and the disturbance level low; (ii) stress-tolerant strategy (S), advantageous where resources are scarce, conditions severe and highly variable, but disturbance is uncommon; and (iii) ruderal strategy (R), advantageous where resources are abundant and conditions not extreme, but the disturbance frequency is high.
Taxa of the Czech flora were assigned to life strategies based on the method proposed by Pierce et al. (2017). The life strategies calculated using this method represent the trade-off in resource investment between three key leaf traits: leaf area (LA; high in competitive taxa), leaf dry matter content (LDMC; high in stress-tolerant taxa) and specific leaf area (SLA; high in ruderal taxa). Scores that express the degree of C-, S- and R-selection are calculated from these traits. These scores are expressed on a percentage scale, and the sum of the three scores for individual taxa is 100%. Based on these scores, the taxa are assigned to the basic primary strategies C, S and R, intermediate strategies CS, CR, SR and CSR, and transitions between them, e.g. C/CS or SR/CSR (sensu Grime 1979). The data on leaf traits for these calculations or calculated values were taken from the LEDA database (Kleyer et al. 2008) and some other sources (Bjorkman et al. 2018, Dayrell et al. 2018, Findurová 2018, Tavşanoğlu & Pausas 2018, Wang et al. 2018, Guo et al. 2019). The Pladias database contains both the score values for the three categories C, S, R and the categorized life strategies.
Guo W.-Y. & Pierce S. (2019) Life strategy. – www.pladias.cz.
Bjorkman A. D., Myers-Smith I. H., Elmendorf S. C. et al. (2018) Tundra Trait Team: A database of plant traits spanning the tundra biome. – Global Ecology and Biogeography 27: 1402–1411.
Dayrell R. L., Arruda A. J., Pierce S., Negreiros D., Meyer P. B., Lambers H. & Silveira F. A. (2018)
Ontogenetic shifts in plant ecological strategies. – Functional Ecology 32: 2730–2741.
Findurová A. (2018) Variabilita listových znaků SLA a LDMC vybraných druhů rostlin České republiky [Variability
of leaf traits SLA and LDMC in selected species of the Czech flora]. – Master thesis, Masaryk University, Brno.
Grime J. P. (1974) Vegetation classification by reference to strategies. – Nature 250: 26–31.
Grime J. P. (1979) Plant strategies and vegetation processes. – Wiley, Chichester.
Kleyer M., Bekker R. M., Knevel I. C., Bakker J. P., Thompson K., Sonnenschein M., Poschlod P., van
Groenendael J. M., Klimeš L., Klimešová J., Klotz S., Rusch G. M., Hermy M., Adriaens D., Boedeltje G.,
Bossuyt B., Dannemann A., Endels P., Götzenberger L., Hodgson J. G., Jackel A. K., Kühn I., Kunzmann D.,
OzingaW. A., Romermann C., Stadler M., Schlegelmilch J., Steendam H. J., Tackenberg O., Wilmann B.,
Cornelissen J. H. C., Eriksson O., Garnier E. & Peco B. (2008) The LEDA Traitbase: a database of life-history
traits of the Northwest European flora. – Journal of Ecology 96: 1266–1274.
Pierce S., Negreiros D., Cerabolini B. E. L., Kattge J., Díaz S., Kleyer M., Shipley B., Wright S. J.,
Soudzilovskaia N. A., Onipchenko V. G., van Bodegom P. M., Frenette-Dussault C., Weiher E., Pinho B. X.,
Cornelissen J. H. C., Grime J. P., Thompson K., Hunt R., Wilson P. J., Buffa G., Nyakunga O. C., Reich P. B.,
CaccianigaM., Mangili F., Ceriani R. M., Luzzaro A., Brusa G., Siefert A., Barbosa N. P. U., Chapin F. S.,
Cornwell W. K., Fang J., Fernandes G. W., Garnier E., Le Stradic S., Peńuelas J., Melo F. P. L., Slaviero A.,
Tabarelli M. & Tampucci D. (2017) A global method for calculating plant CSR ecological strategies
applied across biomes world-wide. – Functional Ecology 31: 444–457.
Tavşanoğlu Ç. & Pausas J. G. (2018) A functional trait database for Mediterranean Basin plants. – Scientific
Data 5: 180135.
Grime (1974, 1979) distinguished three basic ecological strategies of plants: (i) competitive strategy (C), advantageous in stable habitats where resources are abundant, conditions not extreme and the disturbance level low; (ii) stress-tolerant strategy (S), advantageous where resources are scarce, conditions severe and highly variable, but disturbance is uncommon; and (iii) ruderal strategy (R), advantageous where resources are abundant and conditions not extreme, but the disturbance frequency is high.
Taxa of the Czech flora were assigned to life strategies based on the method proposed by Pierce et al. (2017). The life strategies calculated using this method represent the trade-off in resource investment between three key leaf traits: leaf area (LA; high in competitive taxa), leaf dry matter content (LDMC; high in stress-tolerant taxa) and specific leaf area (SLA; high in ruderal taxa). Scores that express the degree of C-, S- and R-selection are calculated from these traits. These scores are expressed on a percentage scale, and the sum of the three scores for individual taxa is 100%. Based on these scores, the taxa are assigned to the basic primary strategies C, S and R, intermediate strategies CS, CR, SR and CSR, and transitions between them, e.g. C/CS or SR/CSR (sensu Grime 1979). The data on leaf traits for these calculations or calculated values were taken from the LEDA database (Kleyer et al. 2008) and some other sources (Bjorkman et al. 2018, Dayrell et al. 2018, Findurová 2018, Tavşanoğlu & Pausas 2018, Wang et al. 2018, Guo et al. 2019). The Pladias database contains both the score values for the three categories C, S, R and the categorized life strategies.
Guo W.-Y. & Pierce S. (2019) Life strategy. – www.pladias.cz.
Bjorkman A. D., Myers-Smith I. H., Elmendorf S. C. et al. (2018) Tundra Trait Team: A database of plant traits spanning the tundra biome. – Global Ecology and Biogeography 27: 1402–1411.
Dayrell R. L., Arruda A. J., Pierce S., Negreiros D., Meyer P. B., Lambers H. & Silveira F. A. (2018)
Ontogenetic shifts in plant ecological strategies. – Functional Ecology 32: 2730–2741.
Findurová A. (2018) Variabilita listových znaků SLA a LDMC vybraných druhů rostlin České republiky [Variability
of leaf traits SLA and LDMC in selected species of the Czech flora]. – Master thesis, Masaryk University, Brno.
Grime J. P. (1974) Vegetation classification by reference to strategies. – Nature 250: 26–31.
Grime J. P. (1979) Plant strategies and vegetation processes. – Wiley, Chichester.
Kleyer M., Bekker R. M., Knevel I. C., Bakker J. P., Thompson K., Sonnenschein M., Poschlod P., van
Groenendael J. M., Klimeš L., Klimešová J., Klotz S., Rusch G. M., Hermy M., Adriaens D., Boedeltje G.,
Bossuyt B., Dannemann A., Endels P., Götzenberger L., Hodgson J. G., Jackel A. K., Kühn I., Kunzmann D.,
OzingaW. A., Romermann C., Stadler M., Schlegelmilch J., Steendam H. J., Tackenberg O., Wilmann B.,
Cornelissen J. H. C., Eriksson O., Garnier E. & Peco B. (2008) The LEDA Traitbase: a database of life-history
traits of the Northwest European flora. – Journal of Ecology 96: 1266–1274.
Pierce S., Negreiros D., Cerabolini B. E. L., Kattge J., Díaz S., Kleyer M., Shipley B., Wright S. J.,
Soudzilovskaia N. A., Onipchenko V. G., van Bodegom P. M., Frenette-Dussault C., Weiher E., Pinho B. X.,
Cornelissen J. H. C., Grime J. P., Thompson K., Hunt R., Wilson P. J., Buffa G., Nyakunga O. C., Reich P. B.,
CaccianigaM., Mangili F., Ceriani R. M., Luzzaro A., Brusa G., Siefert A., Barbosa N. P. U., Chapin F. S.,
Cornwell W. K., Fang J., Fernandes G. W., Garnier E., Le Stradic S., Peńuelas J., Melo F. P. L., Slaviero A.,
Tabarelli M. & Tampucci D. (2017) A global method for calculating plant CSR ecological strategies
applied across biomes world-wide. – Functional Ecology 31: 444–457.
Tavşanoğlu Ç. & Pausas J. G. (2018) A functional trait database for Mediterranean Basin plants. – Scientific
Data 5: 180135.
The months of the beginning and end of flowering in the Czech Republic are given. The data were taken from the Key to the Flora of the Czech Republic (Kaplan et al. 2019).
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.
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.
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.