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Mabea dalyana (Euphorbiaceae-Hippomaneae): a new subshrub with xylopodia endemic to the savannas of the Brazilian Amazon

ABSTRACT

During fieldwork in the Campos Amazônicos National Park, Amazonas state, Brazil, a new endemic species of Mabea was collected in savanna areas. Field collections and specimens in RON, MG, and HRCB were analyzed. To understand the species distribution and verify possible areas of occurrence, niche modeling was conducted using the sdm package in R. Mabea dalyana, the new species is a subshrub with xylopodia and reduced size (less than 1 m height) and small, yellow thyrses. There are several allopatric species of Mabea growing in Amazonian savannas, some widespread but others locally restricted, such as M. uleana from central Amazonia that has some superficial resemblance in leaves and inflorescences but can be distinguished from M. dalyana by pubescent adaxial leaf surface (vs. glabrous), 12-21 submarginal glands (vs. 10 submarginal glands), thyrse brownish to red (vs. yellow thyrse) and conspicuous caruncle (vs. caruncle inconspicuous). M. dalyana is endemic to hyperseasonal savanna, very well adapted to savanna, and fire tolerant. It has notable characteristics, such as a subshrub habit, a xylopodium, glabrous leaves, and sepals noticeably larger than the ovary.

Keywords:
campos amazônicos; fire tolerance; Mabea sect. Mabea; niche modelling; taxonomy

Introduction

Mabea is a genus of Euphorbiaceae with ca. 40 species, and the largest and most diverse genus in the tribe Hippomaneae (Esser 1993Esser H-J. 1993. New species and a new combination in Mabea Aublet (Euphorbiaceae) from South America. Novon 3: 341-351.; 1994Esser H-J. 1994. Systematisch estudienan den Hippomaneae Adr. Jussieu ex Bartling (Euphorbiaceae), insbesondere den Mabeinae Pax & K. Hoffm. PhD thesis, Universität Hamburg, Hamburg.; 2001Esser H-J. 2001. Tribes Hippomaneae, Hureae, Pachystromateae. In: Radcliffe-Smith A. (ed.) Genera Euphorbiacearum. Kew, London, Royal Botanic Gardens . p. 352-397.). The number of species could even be higher because of several still undescribed taxa (Esser 1994Esser H-J. 1994. Systematisch estudienan den Hippomaneae Adr. Jussieu ex Bartling (Euphorbiaceae), insbesondere den Mabeinae Pax & K. Hoffm. PhD thesis, Universität Hamburg, Hamburg.; 2012Esser H-J. 2012. The tribe Hippomaneae in Brazil. Rodriguésia 63: 209-225.). Currently, 25 species are recorded for Brazil, of which five are endemic to the country (Esser 1994Esser H-J. 1994. Systematisch estudienan den Hippomaneae Adr. Jussieu ex Bartling (Euphorbiaceae), insbesondere den Mabeinae Pax & K. Hoffm. PhD thesis, Universität Hamburg, Hamburg.; 2000Esser H-J. 2000. Mabea Aubl. In: Govaerts R, Frodin DG, Radcliffe-Smith A. (eds.) World checklist and bibliography of Euphorbiaceae (with Pandaceae). Kew, London, Royal Botanic Gardens. p. 1071-1077.; Cordeiro et al. 2020Cordeiro I, Esser H-J, Pscheidt AC. 2020. Mabea in flora do Brasil 2020. Jardim Botânico do Rio de Janeiro. http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB17587. 29 Mar. 2021.
http://floradobrasil.jbrj.gov.br/reflora...
).

According to Esser (1994Esser H-J. 1994. Systematisch estudienan den Hippomaneae Adr. Jussieu ex Bartling (Euphorbiaceae), insbesondere den Mabeinae Pax & K. Hoffm. PhD thesis, Universität Hamburg, Hamburg.; 2012Esser H-J. 2012. The tribe Hippomaneae in Brazil. Rodriguésia 63: 209-225.), Mabea is characterized by brownish to reddish dendritic trichomes, in particular on the densely tomentose ovaries and fruits, pistillate flowers with usually six (rarely seemingly three when reduced) sepals and a distinct stylar columns, and staminate flowers with five fused sepals and a large number (sometimes up to ca. 100) of stamens. The genus is currently divided, by the morphological data, into two sections, Mabea sect. Spiculigerae, with two species (M. angustifolia and M. fistulifera) and Mabea sect. Mabea, including all remaining species (Esser 1994Esser H-J. 1994. Systematisch estudienan den Hippomaneae Adr. Jussieu ex Bartling (Euphorbiaceae), insbesondere den Mabeinae Pax & K. Hoffm. PhD thesis, Universität Hamburg, Hamburg.; 2012Esser H-J. 2012. The tribe Hippomaneae in Brazil. Rodriguésia 63: 209-225.). The species of Mabea can be distinguished by leaf glands, venation, pubescence, bracts, size of inflorescence, sepals, and fruit. Still, most of the species can be easily recognized by leaf characters (Esser 2012Esser H-J. 2012. The tribe Hippomaneae in Brazil. Rodriguésia 63: 209-225.).

Here we present a taxonomic novelty of Mabea: the first species to be described in 20 years (Martínez Gordillo et al. 2000Martínez Gordillo M, Jiménez JR, Cruz RD. 2000. El género Mabea (Euphorbiaceae) en México. Anales del Instituto de Biología Universidad Nacional Autónoma de México, Série Botánica 71: 87-95.). This new species was found in Amazonian savanna in the southern part of the Amazonas state, Brazil. Also, the potential distribution and conservation status are analyzed and discussed, contributing to the spatial context of this Amazonian novelty.

Materials and methods

Study area

Mabea dalyana was discovered during four field expeditions between February 2018 and August 2019 to the Campos Amazônicos Savanna Enclave (CASE), a major enclave of savanna vegetation in the Brazilian Meridional Amazonian (Fig. 1A, B). The CASE has a total area of 4,342 km2 almost entirely integrated as a protected area according to Brazilian laws, with 47 % belonging to the limits of Campos Amazônicos National Park (CANP), 46 % and 5 % in the Tenharim Marmelos Indigenous Land and Tenharim Igarapé Preto Indigenous Land, respectively (Fig. 1B). CASE is a continuous area of the predominance of savanna environments (Fig. 1C). It is located in a region dominated by rainforest vegetation, classified as Disjunct Amazonian Savanna, one of the seven provinces of Cerrado described by Ratter et al. (2003Ratter JA, Bridgewater S, Ribeiro JF. 2003. Analysis of the floristic composition of the Brazilian cerrado vegetation: comparison of the woody vegetation of 376 areas. Edinburgh Journal of Botany 60: 57-109.). The topography is composed of flat slopes, dominated by dystrophic soils (neosoils marked by the presence of plinthite in the B horizon) (ICMBio 2016ICMBio - Instituto Chico Mendes de Conservação e Biodiversidade. 2016. Plano de manejo- parque nacional dos campos amazônicos. Ministério do Meio Ambiente (MMA), Brasília, Brasil. https://www.icmbio.gov.br/portal/images/stories/plano-de-manejo/encarte_4_planejamento_do_parna_campos_amazonicos_plano_de_majeno.pdf.
https://www.icmbio.gov.br/portal/images/...
). The regional climatic conditions are characterized by high medium annual temperatures (between 24 ºC and 28 ºC) and annual precipitation of ca. 2000 mm. Between November and March, it is characterized by distinct periods of rain, whereas May to September is a dry season; the months from October to April usually correspond to a transition period between these two seasons (Marengo et al. 2001Marengo JA, Liebmann B, Kousky VE, Filizola NP, Wainer IC. 2001. Onset and end of the rainy season in the Brazilian Amazon Basin. Journal of Climate 14: 833-852.).

Figure 1
Campos Amazônicos National Park (CANP). A. Amazonia limits with the indication of CANP. B. Location of the collection points of Mabea dalyana in the south of the Brazilian Amazon, inside the Campos Amazônicos Savanna Enclave (CASE). C. Typical landscape of the Amazonian savanna inside the CANP. Grasslands and savanna predominate in almost all areas where Mabea dalyana occurs, while forests are mainly found in water bodies' proximity. A and B Background image: ©Esri, DigitalGlobe, GeoEye, i-cubed, USDA, USGS, AEX, Getmapping, Aerogrid, IGN, IGP, Swisstopo, and the GIS User Community. C Photo: D. B. Alves in August 2019.

Herbarium material and methods - The specimens of this new species were studied in the field and in the herbaria RON and MG, acronyms following Thiers (2021Thiers B. 2021, continuously updated. Index Herbariorum: A global directory of public herbaria and associated staff. New York Botanical Garden’s Virtual Herbarium. http://sweetgum.nybg.org/ih/. 29 Mar. 2021.
http://sweetgum.nybg.org/ih/...
, continuously updated). The collection of HRCB was analyzed from images sent by the curator. Specimens were hydrated and analyzed with a stereo microscope, which was connected to a camera.

Niche modeling - The potential distribution of M. dalyana was modeled over the natural savanna and grassland areas of Amazonia (derived from MAPBIOMAS 2020MAPBIOMAS. 2020. Map Biomas Amazonia project - Collection 2.0 of annual maps of coverage and land use from 1985 to 2018 of the pan-amazon. http://mapbiomas.org/. 01 Jul. 2020.
http://mapbiomas.org/...
) using the ‘sdm’ package (Naimi & Araújo 2016Naimi B, Araújo MB. 2016. Sdm: A Reproducible and Extensible R Platform for Species Distribution Modelling. Ecography 39: 368-75. ) in R. As input, 17 climatic and 24 soil variables were obtained from the Worldclim 2 (Fick & Hijmans 2017Fick SE, Hjmans RJ. 2017. WorldClim 2: New 1‐km spatial resolution climate surfaces for global land areas. International Journal of Climatology 37: 4302-4315. ), and Soil Grids (Hengl et al. 2014Hengl T, Jesus JM, MacMillan RA, et al. 2014. SoilGrids1km - global soil information based on automated mapping. PLOS ONE 9: e105992. doi: 10.1371/journal.pone.0105992
https://doi.org/10.1371/journal.pone.010...
) databases, all with a 1 km spatial resolution, and seven location points were used as current presence data (three from voucher collections and four from field inventories, see Tab. S1 in supplementary material), all of them within a distance greater than 2 km from each other (Fig. 1B). Variance inflation factor (VIF) analysis (Marquaridt 1970Marquaridt DW. 1970. Generalized inverses, ridge regression, biased linear estimation, and nonlinear estimation. Technometrics 12: 591-612. ) was used to avoid collinearity (using a threshold of 0.7), finally selecting nine variables (climate - Mean Diurnal Range Temperature, Isothermality, Temperature Seasonality, Precipitation of Wettest Month, and Precipitation of Driest Month; soil (for depthsof 0-30 cm) - Available Soil Water Capacity, Weight Percentage of the Clay Particles, Volumetric Percentage of Coarse Fragments, and Weight Percentage of the Silt Particles). A presence-background model was configured using 100 pseudo-absence points, randomly assigned (‘gRandom’), and 10 runs per method (Barbet-Massin et al. 2012Barbet-Massin M, Jiguet F, Albert CH, Thuiller W. 2012. Selecting pseudo-absences for species distribution models: How, where and how many? Methods in Ecology and Evolution 3: 327-338. ). The suitability distribution map was derived from an ensemble of 3 different methods: generalized linear model - GLM (McCulagh & Nelder 1989McCulagh P, Nelder JA. 1989. Generalized linear models. 2nd edn. Boca Raton, Chapman & Hall/CRC.), random forest - RF (Breiman 2001Breiman L. 2001. Random forests. Machine Learning 45: 5-32. ), and Support Vector Machine - SVM (Cortes & Vapnik 1995Cortes C, Vapnik V. 1995. Support-vector networks. Machine Learning 20: 273-297.); all of them implemented in the ‘sdm’ package. Finally, the area under the curve (AUC) of the receiver operating characteristic (ROC) was used to assess the model, based on bootstrapping replications (Hastie et al. 2009Hastie T, Tibshirani R, Friedman J. 2009. The elements of statistical learning: data minig, inference, and prediction. 2nd. edn. Stanford, Springer-Verlag.), and Pearson correlation tests (r) were applied to explore the influence of the variables used in the final model.

Conservation status and ecology - We used the Geospatial Conservation Assessment Tool (GEOCAT) (Bachman et al. 2011Bachmann S, Moat J, Hill AW, De la Torre J, Scott B. 2011. Supporting red list threat assessments with geocat: geospatial conservation assessment tool. ZooKeys 150: 117-126. ) with a cell grid of 2 km2, providing information about the area of occupancy and the extent of occurrence of the new species. The conservation status was evaluated following the Red List criteria of the International Union for the Conservation of Nature (IUCN 2019IUCN - International Union for Conservation of Nature. 2019. Guidelines for using the IUCN red list categories and criteria. Version 14. Prepared by the standards and petitions sub-committee. https://nc.iucnredlist.org/redlist/content/attachment_files/RedListGuidelines.pdf.
https://nc.iucnredlist.org/redlist/conte...
). Complementary data on the history of forest fires of each locality visited were verified by the database of burnt areas of the CASE (Alves & Pérez-Cabello 2017Alves DB, Pérez-Cabello F. 2017. Multiple remote sensing data sources to assess spatio-temporal patterns of fire incidence over campos amazônicos savanna vegetation enclave (Brazilian Amazon). Science of the Total Environment 601-602: 142-158.), estimating possible influences on the recursion of these factors on the presence and distribution of the species.

Results and discussion

Taxonomic treatment

Mabea dalyana Bigio, Esser & Secco, sp. nov.

Type: BRAZIL, Amazonas: Manicoré, Parque Nacional dos Campos Amazônicos, 8°29’24” S, 61°30’25” W, 24 Aug. 2019, fl, fr, C.B. Anjos 200 (holotype: RON; isotype: MG). (Figs. 2, 3).

Figure 2
Mabea dalyana (Anjos 200): A. Habit; black arrow indicates part of the xylopodium. B. Staminate cymule. C. Staminate flower. D. Pistillate flower. E. Fruit. F. Seed with reduced caruncle.

Figure 3
Mabea dalyana in the field (Anjos 200): A. Habit. B. Inflorescence. C. Fruit. D. Xylopodium. E. Habitat, white arrows point to three small individuals of M. dalyana. E. from Campos Amazônicos National Park. Photo C.B. Anjos in August 2019.

Mabea dalyana is a subshrub less than 1m height, with xylopodia elongate, blades ovate-elliptic, glabrous, abaxial surface with 3-6 (10) submarginal glands. Staminate bracts cymules with a pair of stipitate glands; pistillate sepals 1.3-2 mm long, longer than the ovary.

Subshrub up to 45 cm tall; xylopodia elongate, cylindric, with longitudinal striations. Branches cylindric, glabrous, with longitudinal striations. Leaves alternate, blades ovate-elliptic, 4.0-8.2 × 1.7-3.6 cm, chartaceous to slightly coriaceous, base rounded to obtuse, margin almost entire, but serrulate towards the apex, slightly revolute, apex acute to acuminate, glabrous on both surfaces, secondary veins in 6-9 pairs, brochidodromous, well visible on both surfaces; abaxial submarginal glands 3-6 (10), ca. 0.25-0.3 mm in diameter and separated from the margin by ca. their own diameter; petiole 2-4 mm long, glabrous, adaxially canaliculate; stipules 2.5-3 × 0.8-1 mm, deltoid, glabrous. Inflorescences yellow thyrses, unbranched or sometimes compound with usually 2-3 branches, but then only one branch flowering at any given time; central axes glabrous, each branch with the staminate part 1-5 × 0.7-2 cm, bracts of staminate cymules 0.8-1.2 mm long, base obtuse and apex acuminate, with a pair of stipitate glands 0.8-1.5 mm long; at base with (1-)2 pistillate flowers, bracts with 2 basal glands, 0.1-0.3 mm long. Staminate flowers 2-3 per cymule; pedicel pubescent, 3-7 mm long, free; calyx with deltoid lobes 1.0-1.2 mm long; stamens 15-20 per flower. Pistillate flowers solitary, pedicel 5-8 mm long, enlarging in fruit to 12 mm long; calyx 6, free, eglandular; sepals, lanceolate-ovate, 1.3-2 mm long, base obtuse, apex acuminate, longer than the ovary; ovary 0.8-1.3 mm long, globose, tomentose, stylar column 2-3 mm long, pubescent, stigmas 5-6 mm long, recurved. Fruits subglobose, reddish-brown, 0.8-1 × 0.8-1.2 cm, tomentose, slightly sulcate, smooth. Seeds 7 × 5 × 3 mm, caruncle inconspicuous, the transversal hilum dark brown.

Distribution and niche modeling - Mabea dalyana has been observed in seven different locations inside CANP, in the municipalities of Manicoré and Novo Aripuanã (Amazonas state). Based on climatic and edaphic datasets and the observed characteristics at the known presence data points, a potential distribution of M. dalyana was modeled over all natural savanna and grasslands areas of Amazonia (Fig. 4A, B). Available soil water capacity (r = 0.71) and temperature seasonality variations (r = -0.42) were the variables that most influenced the final model, suggesting the existence of specific regional edaphic-climatic combinations that favour the presence of the species.

Figure 4
Potential distribution of Mabea dalyana within the Amazonian savanna and grassland. A. Overview map with an indication of the habitat suitability for M. dalyana in the Amazon. B. Close-up of the modeled areas with the highest suitability levels of habitat suitability (orange to red) as well as the location of the M. dalyana collection points inside the CANP (black dots). Background image: ©Esri, DigitalGlobe, GeoEye, i-cubed, USDA, USGS, AEX, Getmapping, Aerogrid, IGN, IGP, Swisstopo, and the GIS User Community.

In general terms, the model evaluation presents a high value of AUC (0.93). The areas with the highest occurrence suitability are located in the southern Brazilian Amazon, closely associated with the region of collection points. These highest suitability levels (Fig. 4B) were observed in almost all savanna enclaves of CANP (08°27’24” S, 61°33’20” W), including the Indigenous Lands of Tenharim Marmelos and Tenharim Igarapé Preto in the vicinity.

Other areas with moderate-high suitability can be found in the surrounding regions, and well conserved areas, like the savanna ecotones of the Guariba Statal Park (08°45’79’’ S, 60°38’22’’ W), the Mapinguari National Park (07°51’00” S, 63°51´23” W) and the Ecology Station of Cuniã (08°11’46” S, 63°51´23” W); however, we did not find M. dalyana in these areas. The first one is near CANP and has higher suitability, and we still did not collect there. The others two conservation units we already made some expedition and we did not find it, probably because they have less suitability.

In other areas of Amazonia, the suitability is generally rated lower, where some specific areas can be highlighted as the portions of Marajó Island (49°04’10” W, 00°38’31” S), in the north of Brazil, and sectors of the National Park of Yapacaná (67°04’03” W, 03°55’33” N) in Venezuela, where, for instance, M. frutescens occurs. Even with some constraints related to the low number of collection points and his geographic concentration in terms of the Amazonia region, these potential distribution models can still guide new collection campaigns in other suitable areas.

Habitat and ecology - Mabea dalyana occurs along an environmental gradient from seasonal savannas, subjected to annual drought stress, to areas of hyperseasonal savannas sensuBatalha et al. (2005Batalha MA, Silva IA, Cianciaruso MV, Delitti WBC. 2005. Hyperseasonal cerrado, a new Brazilian vegetation form. Brazilian Journal of Biology 65: 735-738. ), that in addition to drought, are also subjected to regular flooding during the rainy season. M. dalyana seems to be well adapted to fire, drought, and inundation, as seen by the presence of xylopodia that allow the accumulation of nutrients for rapid growth after the loss of branches and leaves. Areas where M. dalyana were collected were subjected to different fire patterns during the last years (Alves & Pérez-Cabello 2017Alves DB, Pérez-Cabello F. 2017. Multiple remote sensing data sources to assess spatio-temporal patterns of fire incidence over campos amazônicos savanna vegetation enclave (Brazilian Amazon). Science of the Total Environment 601-602: 142-158.), suggesting that this species is adapted to diverse frequency of fires.

Three of these localities are included in permanent experimental plots to study the effects of fires in the savannas. Direct observations executed in these experimental plots suggest a significant percentage of individuals with inflorescences in plots recently burnt, in contrast, to control plots (not burnt), an issue that will be analyzed in more detail in future studies (Alves in prep.). Relationships between the influence of fires, the flowering of the plants, and the presence of xylopodia and other structures for nutrient storage, are also illustrated in other studies of plants the herbaceous layer in areas of tropical savannas (Miranda et al. 2004Miranda HS, Sato MN, Andrade SMA, Haridasan M, Morais HC. 2004. Queimadas de Cerrado caracterização e impactos. In: Aguiar LMS, Camargo AJA. (eds.) Cerrado - ecologia. Brasília, Embrapa Cerrados. p. 69-123.; Fidelis et al. 2019Fidelis A, Rosalem P, Zanzarini V, Camargos LS, Martins AR. 2019. From ashes to flowers: a savanna sedge initiates flowers 24 h after fire. Ecology 100: e02648. doi: 10.1002/ecy.2648
https://doi.org/10.1002/ecy.2648...
) and correspond to the patterns observed with M. dalyana.

Phenology-Mabea dalyana were collected with flowers and fruit in April, July and August.

Etymology - The name Mabea dalyana honours Dr. Douglas Charles Daly, botanist of The New York Botanical Garden, who contributed significantly to our knowledge of the Amazonian flora with undeviating energy, and invigorated our knowledge of the state of Rondônia, and who aided much in the education of new enthusiasts of the Scientia amabilis.

IUCN conservation assessment - Mabea dalyana has an area of occupancy (AOO) of 28 km2, and an extent of occurrence (EOO) of 130 km2, and has been recorded in seven different localities within the CANP. These conditions indicate that the species can be classified as Endangered under Criterion B. The species has a restricted distribution, with dense subpopulations, and occurs in an extensive area of well-protected savanna vegetation with low current anthropogenic influences. Considering that the species depends on a protected area, it seems appropriate to assessed as Near Threatened (NT) regarding its distribution and number of locations, meeting the criteria B1a+B2a.

Comments - Mabea dalyana belongs to Mabea sect. Mabea because of the absence of an apical awn on the leaf blade, the leaves being not papillate below, the sepals of mature pistillate flowers not imbricate, and in particular because of the 3-flowered staminate cymules with free pedicels. Mabea dalyana seems to be restricted to savannas of the southern parts of Amazonia (see the results of niche modeling) and exhibits some characters that are certainly adaptations to the peculiar habitat conditions (low growth, xylopodia). Similar characters are also found in few other species of white sand savannas north of the Amazon, e.g., M. frutescens, occurring in Venezuela and Colombia. Mabea dalyana differs from the M. frutescens in acute-acuminate leaves and yellowish inflorescences, tyrses ca. 1-5 cm long and, pistillate flowers with sepals longer than ovary (vs. apically rounded-mucronate leaves and reddish-brownish thyrses ca. 6-10 cm long and, pistillate flowers with shorter sepals than ovary). These two species are probably not phylogenetics closely related. The morphological characteristics are probably parallel adaptations because of environmental factors, but the species relationships within the genus are mostly unsolved.

There are several allopatric species of Mabea growing in Amazonian savannas, some widespread but others locally restricted, such as M. uleana from central Amazonia that has some superficial resemblance in leaves and inflorescences but can be distinguished from M. dalyana by pubescent adaxial leaves (vs. glabrous leaves), 12-21 submarginal glands (vs. 10 submarginal glands), thyrse brownish to red (vs. yellow thyrse) and caruncle distinguished (vs. indistinctly caruncle). For other characters, see Table 1. The collection Anjos 73 shows some pistillate flowers with 4 or 5 stigmas, very probably only an aberrant specimen.

Table 1
Morphological comparison between Mabea dalyana and similar species.

Note that M. dalyana was discovered after collections made within the fire monitoring project at CANP were made in the years 2018 and 2019. When we studied the material and checked other collections, we found the specimen Lombardi 10046 made during the Park management plan in 2013. This discovery reinforces the need to make more collections in the Amazon and to have more taxonomists in the region to identify the plants (Sobral & Stehmann 2009Sobral M, Stehmann JR. 2009. An analysis of new angiosperm species discoveries in Brazil (1990-2006). Taxon 58: 227-232.; Miliken et al. 2010Milliken W, Zappi DC, Sasaki D, Hopkins MJG, Pennington RT. 2010. Amazon vegetation: how much don't we know and how much does it matter? Kew Bulletin 65: 691-709.; Gasper et al. 2020Gasper A, Stehmann JR, Roque N, Bigio NC, Sartori ALB, Grittz GS. 2020. Brazilian herbaria: an overview. Acta Botanica Brasilica 34: 352-359. ).

Additional material examined (paratype). BRAZIL. Amazonas: Mun. Manicoré, Parque Nacional dos Campos Amazônicos, 8(28’20” S, 61(38’53” W, 31 July 2018, fl, fr, C.B. Anjos 73 (RON, MG); 8(28’37” S, 61(38’58” W, 02 Apr. 2018, fl, F. Bonadeu 1082 (RON, MG); Nova Aripuanã, 8°34’55” S, 61°24’26” W, 29 July 2013, fl., J. Lombardi 10046 (HRCB).

Acknowledgements

Thanks are due to Dr. Sebastian Drude and Pablo Diener, for translations of German texts; to the artist, Carlos Alvarez, for the drawing; to Ana Carolina Devides Castello, for help with the niche modelling; to the staff all of the CANP and their respective Fire Brigade, in particular to Bruno Cambraia; to the CNPq for a doctoral grant to Narcísio Bígio (141313/2018-8) and for financial support of the project realized in the CANP (441968/2018-0); for the FAPESP (2019/07357-8).

References

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  • Bachmann S, Moat J, Hill AW, De la Torre J, Scott B. 2011. Supporting red list threat assessments with geocat: geospatial conservation assessment tool. ZooKeys 150: 117-126.
  • Barbet-Massin M, Jiguet F, Albert CH, Thuiller W. 2012. Selecting pseudo-absences for species distribution models: How, where and how many? Methods in Ecology and Evolution 3: 327-338.
  • Batalha MA, Silva IA, Cianciaruso MV, Delitti WBC. 2005. Hyperseasonal cerrado, a new Brazilian vegetation form. Brazilian Journal of Biology 65: 735-738.
  • Breiman L. 2001. Random forests. Machine Learning 45: 5-32.
  • Cordeiro I, Esser H-J, Pscheidt AC. 2020. Mabea in flora do Brasil 2020. Jardim Botânico do Rio de Janeiro. http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB17587 29 Mar. 2021.
    » http://floradobrasil.jbrj.gov.br/reflora/floradobrasil/FB17587
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    » https://doi.org/10.1002/ecy.2648
  • Gasper A, Stehmann JR, Roque N, Bigio NC, Sartori ALB, Grittz GS. 2020. Brazilian herbaria: an overview. Acta Botanica Brasilica 34: 352-359.
  • Hastie T, Tibshirani R, Friedman J. 2009. The elements of statistical learning: data minig, inference, and prediction. 2nd. edn. Stanford, Springer-Verlag.
  • Hengl T, Jesus JM, MacMillan RA, et al 2014. SoilGrids1km - global soil information based on automated mapping. PLOS ONE 9: e105992. doi: 10.1371/journal.pone.0105992
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Publication Dates

  • Publication in this collection
    11 Mar 2022
  • Date of issue
    2022

History

  • Received
    01 Feb 2021
  • Accepted
    10 May 2021
Sociedade Botânica do Brasil SCLN 307 - Bloco B - Sala 218 - Ed. Constrol Center Asa Norte CEP: 70746-520 Brasília/DF. - Alta Floresta - MT - Brazil
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