|
Endemic to Brazil and threatened |
|
|
|
|
|
Seligeriaceae |
*Atractylocarpus brasiliensis (Müll.Hal.) R.S. Williams |
EN |
EN |
B1ab(i, ii, iii) |
1.1; 2.2; 7.1.1; 11.2; 11.3 |
This species is endemic to the Atlantic Forest (occurring in BA and RJ states) (Flora e Funga do Brasil, 2023Flora e Funga do Brasil. 2023. Dicranaceae in Flora e Funga do Brasil. Jardim Botânico do Rio de Janeiro. https://floradobrasil.jbrj.gov.br/FB96138. 27 Sep. 2023. https://floradobrasil.jbrj.gov.br/FB9613...
). The species has a limited occurrence in high-altitude fields and high mountain forests forming tufts of separated subpopulations. Has an EOO of 549,37 km². Both the species and its region of occurrence are threatened by activities such as urban expansion, agricultural activities, and wildfires that provoque continuing decline in habitat quality, EOO and AOO. The species was exclusively found in the area adjacent to the road between Posto do Marcão and Abrigo Rebouças, specifically in soil with leaf litter or among plants. Furthermore, it was not found in the previously documented localities mentioned in the herbarium samples, indicating a continuing decline in its AOO. |
Seligeriaceae |
Brachydontium notorogenes W.R.Buck & Schaf.-Verw. |
CR |
CR |
B2ab (ii, iii, iv) |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to the INP. Historically found on the trail between Abrigo Rebouças and Agulhas Negras on rock outcrops. That trail was searched, but the species could not be found. Both the species and its region of occurrence are threatened by wildfires and predatory tourism, which has resulted in a continuing decline in its AOO as well as habitat quality; there have been few scientific collection records. The population on the type locality was not found, so we considered it as a continuing decline of its AOO. |
Brachytheciaceae |
Brachythecium poadelphus Müll.Hal.
|
VU |
VU |
B2ab (ii, iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to the Atlantic Forest, with distribution within protected areas established in the states of RJ, MG, and SP. Few records in scientific collections. Has an AOO of 12,000 km², but even though the high-altitude fields of the INP represents one of the best-inventoried areas of the park, this species has not been seen or collected there, which indicates a significant decline in its population size. Both the species and the region in which it occurs suffer from wildfires and excessive tourism, leading to declining habitat quality. |
Ditrichaceae |
Cladastomum robustum Broth. |
VU |
VU |
B2 |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to Serra da Mantiqueira (MG and RJ). Poorly represented in scientific collections. This species evidence the strategy of annual plants, being strongly seasonal with a dormancy phase during which it survives through spore banks. Mortality is determined by abiotic factors (During 1979During HJ. 1979. Life strategies of bryophytes. Lindbergia 5: 2-18.). Glime (2007Glime JM. 2007. Bryophyte Ecology. Vol. I Physiological Ecology. Michigan Technological University and the International Association of Bryologists. https://digitalcommons.mtu.edu/bryophyte-ecology/. 17 Set. 2023. https://digitalcommons.mtu.edu/bryophyte...
) noted that annual species produce cleistocarpous capsules without specialized mechanisms for spore liberation. Has an AOO of 12,000 km² and an EOO of 284,478 km². Both the species and the region of its occurrence suffer from negative impacts from wildfires and excessive tourism that lead to declining habitat quality. |
Ditrichaceae |
*Crumuscus vitalis W.R.Buck & Snider |
EN |
EN |
B1ab(iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to the INP. It grows on rocks along trails, which are habitats of elevated anthropic impact. Life strategy is normally annual and strongly seasonal; mortality is determined by abiotic factors (During 1979During HJ. 1979. Life strategies of bryophytes. Lindbergia 5: 2-18.). It has an EOO of 2,859 km² and an AOO of 16,000 km². Both the species and its region of occurrence are threatened by wildfires and intensive tourism that lead to its continually declining AOO, habitat quality, and numbers of subpopulations. Additionally, during fieldwork it was observed that populations occur in distant patches the subpopulations are highly fragmented. |
Ditrichaceae |
Ditrichum itatiaiae var. brevipes (Müll.Hal.) Paris |
VU |
DD |
|
|
Taxonomic knowledge deficient. The species has not been revised since publication. |
Bruchiaceae |
Eobruchia bruchioides (Müll.Hal.) W.R.Buck
|
VU |
CR |
B1ab(ii, iii) + 2ab(ii, iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to the INP. Distributed exclusively in high-altitude fields. Terricolous, encountered along trail sides, environments experiencing elevated anthropic impacts. Subject to damage from wildfires, trampling, diminishing habitat quality, and excessive tourism. Has an AOO of 4,000 km² and an EOO of 4,000 km². Known from only the type locality with a declining AOO and declining habitat quality. In addition to being poorly represented in scientific collections, it has not been collected recently. |
Dicranaceae |
*Paraleucobryum longifolium subsp. brasiliense (Broth.) P.Müller & J.-P.Frahm |
VU |
VU |
B2ab(iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to the Brazilian Atlantic Forest (RJ and ES). Distributed in high-altitude fields and high-elevation forests. Has an AOO of 12,000 km², and is encountered only in established conservation areas (the Mestre Álvaro Biological Station and the INP). Recently collected along the trail to Agulhas Negras Peak at 2,434 m a.s.l on the trunks of small trees. Both the species and its region of occurrence suffer with the effects of excessive tourism and repeated wildfires, which has led to declines in habitat quality and extension. |
Sphagnaceae |
*Sphagnum exquisitum H.A. Crum |
VU |
VU |
B2ab(ii, iii) |
5.2; 5.2.1; 11.2; 11.3 |
This species is endemic to the Brazilian Atlantic Forest (ES, MG, SP, RJ and SC). In spite of having a extensive EOO (70,608 km²), the species suffers from harvesting and commercialization as it is rarely cultivated but collected in the wild for floriculture use (Rancura et al. 2010Rancura S, Ribeiro MM, Nordi N. 2010. Considerações sobre a coleta de Sphagnum no município de Cananéia, estado de São Paulo, Brasil. Acta Botanica Brasilica 24: 328-334. ; Negrelle et al. 2014Negrelle RRB, Bordignon SE, Ferreira MR, Sampaio LK. 2014. Extrativismo e comercialização de Sphagnum (veludo): Características, implicações socioeconômicas e ecológicas e perspectivas. Revista Brasileira de Horticultura Ornamental 20: 53-66.; Glime 2007Glime JM. 2007. Bryophyte Ecology. Vol. I Physiological Ecology. Michigan Technological University and the International Association of Bryologists. https://digitalcommons.mtu.edu/bryophyte-ecology/. 17 Set. 2023. https://digitalcommons.mtu.edu/bryophyte...
). Additionally, it has an AOO of 60,000 km², and is known from less than 10 locations. Those factors, combined with commercial harvesting, results in the species being threatened. |
Sphagnaceae |
Sphagnum longicomosum Müll.Hal.
|
EN |
VU |
B2ab(ii, iii) |
5.2; 5.2.1; 11.2; 11.3 |
This species is endemic to Brazil, encountered in the Cerrado and the Atlantic Forest (ES, MG, SP, RJ, DF, GO, PR and RS). In spite of its extensive EOO (70,945 km²), the species is not cultivated but is threatened by commercialization and harvesting directly in the field for floriculture use (Rancura et al. 2010Rancura S, Ribeiro MM, Nordi N. 2010. Considerações sobre a coleta de Sphagnum no município de Cananéia, estado de São Paulo, Brasil. Acta Botanica Brasilica 24: 328-334. ; Negrelle et al. 2014Negrelle RRB, Bordignon SE, Ferreira MR, Sampaio LK. 2014. Extrativismo e comercialização de Sphagnum (veludo): Características, implicações socioeconômicas e ecológicas e perspectivas. Revista Brasileira de Horticultura Ornamental 20: 53-66.; Glime 2007Glime JM. 2007. Bryophyte Ecology. Vol. I Physiological Ecology. Michigan Technological University and the International Association of Bryologists. https://digitalcommons.mtu.edu/bryophyte-ecology/. 17 Set. 2023. https://digitalcommons.mtu.edu/bryophyte...
). It has an AOO of 64,000 km², and is known from less than 10 locations, which results in the species being threatened. |
Sphagnaceae |
Sphagnum platyphylloides Warnst. |
VU |
VU |
B1ab(i,ii,iii) |
5.2; 5.2.1; 11.2; 11.3 |
This species is endemic to Brazil, occurs in the Cerrado and the Atlantic Forest (ES, MG, RJ, GO e DF). In spite of its extensive EOO (162,366,682 km²), the species is restricted to mountain tops. It is not cultivated but it is threatened by extractivism and commercialization to attend the floriculture sector (Rancura et al. 2010Rancura S, Ribeiro MM, Nordi N. 2010. Considerações sobre a coleta de Sphagnum no município de Cananéia, estado de São Paulo, Brasil. Acta Botanica Brasilica 24: 328-334. ; Negrelle et al. 2014Negrelle RRB, Bordignon SE, Ferreira MR, Sampaio LK. 2014. Extrativismo e comercialização de Sphagnum (veludo): Características, implicações socioeconômicas e ecológicas e perspectivas. Revista Brasileira de Horticultura Ornamental 20: 53-66.; Glime 2007Glime JM. 2007. Bryophyte Ecology. Vol. I Physiological Ecology. Michigan Technological University and the International Association of Bryologists. https://digitalcommons.mtu.edu/bryophyte-ecology/. 17 Set. 2023. https://digitalcommons.mtu.edu/bryophyte...
). It has na AOO of 24,000km², and is known from less than 10 locations, which results in the species being threatened. |
Sphagnaceae |
*Sphagnum pseudoramulinum H.A. Crum |
VU |
VU |
B2ab(ii, iii) |
5.2; 5.2.1; 11.2; 11.3 |
This species is endemic to the Atlantic Forest (ES, MG, SP, RJ and RS). It has an EOO of 28,792 km². It presents threats arising from extractivism and commercialization, since, in general, they are not cultivated, but extracted directly from nature to meet the demands of the florist service (Rancura et al. 2010Rancura S, Ribeiro MM, Nordi N. 2010. Considerações sobre a coleta de Sphagnum no município de Cananéia, estado de São Paulo, Brasil. Acta Botanica Brasilica 24: 328-334. ; Negrelle et al. 2014Negrelle RRB, Bordignon SE, Ferreira MR, Sampaio LK. 2014. Extrativismo e comercialização de Sphagnum (veludo): Características, implicações socioeconômicas e ecológicas e perspectivas. Revista Brasileira de Horticultura Ornamental 20: 53-66.; Glime 2007Glime JM. 2007. Bryophyte Ecology. Vol. I Physiological Ecology. Michigan Technological University and the International Association of Bryologists. https://digitalcommons.mtu.edu/bryophyte-ecology/. 17 Set. 2023. https://digitalcommons.mtu.edu/bryophyte...
). It has an AOO of 36,000 km², known for less than 10 locations, which places it in a threatened situation. |
Sphagnaceae |
Sphagnum rotundatum Müll.Hal. & Warnst. |
VU |
VU |
B2ab(ii, iii) |
5.2; 5.2.1; 11.2; 11.3 |
This species is endemic to Brazil, present in Cerrado and Atlantic Forest (GO, MG, RJ, SP, PR, SC). It has an EOO of 27,297 km² (RJ, MG) and an AOO of 12,000 km². It presents threats arising from extractivism and commercialization, since, in general, they are not cultivated, but extracted directly from nature to meet the demands of the florist service (Rancura et al. 2010Rancura S, Ribeiro MM, Nordi N. 2010. Considerações sobre a coleta de Sphagnum no município de Cananéia, estado de São Paulo, Brasil. Acta Botanica Brasilica 24: 328-334. ; Negrelle et al. 2014Negrelle RRB, Bordignon SE, Ferreira MR, Sampaio LK. 2014. Extrativismo e comercialização de Sphagnum (veludo): Características, implicações socioeconômicas e ecológicas e perspectivas. Revista Brasileira de Horticultura Ornamental 20: 53-66.; Glime 2007Glime JM. 2007. Bryophyte Ecology. Vol. I Physiological Ecology. Michigan Technological University and the International Association of Bryologists. https://digitalcommons.mtu.edu/bryophyte-ecology/. 17 Set. 2023. https://digitalcommons.mtu.edu/bryophyte...
). It has an AOO of 12,000 km², known for less than 10 locations, which places it in a threatened situation. |
|
Threatened |
|
|
|
|
|
Andreaceae |
*Andreaea acutifolia Hook.f. & Wils. |
NE |
DD |
|
|
This species presents disjunct distribution in the southern hemisphere. Species very similar to A. rupestris, what differentiates the species are the perichaetial leaves. For this reason, it has few collection records or misidentifications. Collecting efforts and investments in scientific research are necessary in order to certify the real geographic distribution of the taxon. |
Andreaceae |
*Andreaea rupestris Hedw. |
VU |
VU |
B2ab(iii) |
6.1; 7.1.1; 11.2; 11.3 |
Wide worldwide distribution, especially in temperate regions. However, in Brazil, it is restricted to the high-altitude fields of the southeast region. It is threatened due to its distribution limited to rocky environments in high-altitude fields, an ecosystem threatened by climate change, excessive tourism and fires, which causes a decrease in habitat quality. It has an AOO of 44,000 km². |
Andreaceae |
*Andreaea subulata Harv.
|
VU |
CR |
A1c; B1b(i,ii,iii,iv) + B1c(i,ii,iii) |
6.1; 7.1.1; 11.2; 11.3 |
Disjunct distribution in the southern hemisphere. It has small populations, restricted to rocky habitats with the presence of water (Gonçalves et al. 2022Gonçalves MTA, Peralta DF, Santos ND. 2022. Rediscovering Andreaea subulata Harv., a critically endangered moss in Brazil. Acta Botanica Brasilica 36: e20220165.). In Brazil, it occurs in RJ state, with recent collection only in Agulhas Negras (INP). In addition, it has shown a reduction in population size in recent decades. It suffers threats due to excessive tourism and fires that reduce the quality of the habitat, and it is threatened due to its ecosystem (high-altitude fields) be threatened by climate change. It has an AOO of < 8,000 km². |
Dicranaceae |
Atractylocarpus longisetus (Hook.) E.B.Bartram
|
VU |
EN |
B1ab(iii)+2ab(iii) |
6.1; 8; 8.1; 8.2.1; 11.2; 11.3 |
Neotropical distribution. However, in Brazil it only occurs in the states of RJ, MG and ES. Found at altitudes ranging from 1,200 to 2,700 m a.s.l. in altitude fields and dense and mixed rain forest, environments that are being degraded by human activities, invasion of exotic species and climate change. It has an EOO of 547.32 km² and is subject to loss and decline in habitat quality as its main threat. |
Seligeriaceae |
*Blindia magellanica Schimp.
|
VU |
EN |
B2ab(ii,iii, iv) |
6.1; 7.1.1; 11.2; 11.3 |
It presents disjunct distribution of temperate regions and tropical mountains. However, in Brazil it occurs only in the state of RJ (INP) and ES (Parque Nacional do Caparaó) in Protected areas. It has an EOO of 1,124,365 km² and an AOO of 12,000km². It is in a situation of threat, as its region of occurrence suffers from excessive tourism and fire, which leads to a decline in habitat quality, in addition to being known for two locations. |
Dicranaceae |
*Campylopus cuspidatus var. dicnemoides (Müll.Hal.) J.-P.Frahm |
VU |
VU |
B2ab(ii, iii) |
6.1; 7.1.1; 11.2; 11.3 |
Despite having a neotropical distribution, in Brazil it occurs only in the states of RJ and SC. It has an EOO of 6,092 km² and an AOO of 12,000km². Frahm (1991)Frahm J-P. 1991. Dicranaceae: Campylopoioidae, Paraleucobryoidae. Flora Neotropica, monograph 54: 1-238. cites the occurrence of the species in the state of AM on Cerro Duida. However, this tepui is located in Venezuela, so it is an erroneous record for the state of AM. The species and its range suffer threats such as fire and predatory tourism, which leads to a continuous decline in AOO, EOO and habitat quality. |
Dicranaceae |
Campylopus densicoma (Müll.Hal.) Paris |
EN |
EN |
B1ab(i,ii,iii) |
6.1; 7.1.1; 11.2; 11.3 |
Despite its wide distribution in the Neotropics, in Brazil the species is restricted to the high-altitude fields of Rio de Janeiro (EOO=273.88 km²). Under-represented in scientific collections. Therefore, a greater collection effort is recommended for the species, in order to know its real geographic distribution. |
Dicranaceae |
*Campylopus jamesonii (Hook.) A.Jaeger |
VU |
VU |
B2ab(ii, iii) |
6.1; 7.1.1; 11.2; 11.3 |
Disjunct distribution between Africa and Neotropics. In Brazil it is mainly known for regions of high-altitude fields in the southeast region (MG, RJ and SP). It has a preferential microenvironment in high-altitude fields at the base of Chusquea sp. Showcasing AOO of 52,000 km². The species and its range suffer threats such as fire and predatory tourism, which leads to a continuous decline in AOO, EOO and habitat quality. |
Ditrichaceae |
*Chrysoblastella chilensis (Mont.) Reimers
|
VU |
EN |
B1ab(iii)+2ab(iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species with Neotropical distribution (He 1998He S. 1998. A Checklist of the mosses of Chile. Journal of the Hattori Botanical Laboratory 85: 103-189.). It presents records in subantarctic islands, such as Tristan da Cunha, Marion Island, South Georgia and Macquarie Island, in addition to New Zealand and southeastern Australia (Larraín 2009Larraín J. 2009. Chrysoblastella R.S.Williams in Musgos de Chile. http://www.musgosdechile.cl. 24 Sep. 2022. http://www.musgosdechile.cl...
). In Brazil, the species occurs in the states of Espírito Santo, Minas Gerais and Rio de Janeiro. In INP it was collected at altitudes above 2100 m a.s.l. It has an EOO of 775,854 km² and an AOO of 12,000 km². The frequency of fire in its occurrence regions is quite significant (INP) and the decline in habitat quality is the main threat to this species. |
Amblystegiaceae |
Drepanocladus perplicatus (Dusén) G. Roth
|
VU |
NT |
|
|
This species is widely distributed in South America. In the resarch by Costa et al. (2005Costa DP, Imbassahy CAA, Silva VPAV. 2005. Diversidade e Importância das Espécies de Briófitas na Conservação dos Ecossistemas do Estado do Rio de Janeiro. Rodriguésia 56: 13-49.), the citation on the voucher was from Drepanocladus brasiliensis Broth., which is a synonym of Warnstorfia exannulata. However, it may be included in some threat category in the near future because it occurs in regions that suffer from urbanization, presence of fire and excessive tourism. |
Fissidentaceae |
Fissidens wallisii Müll.Hal.
|
VU |
LC |
|
|
This species with neotropical distribution, widely distributed in the Atlantic Forest, occurring in the states of ES, MG, RJ, SC and RS. Occurs mainly in rainforest and mixed rainforest. In addition, it is located in protected areas throughout its distribution. |
Pottiaceae |
*Leptodontium flexifolium (Dicks.) Hampe |
VU |
VU |
B1ab(i, ii, iii)+B2ab(i, ii, iii) |
6.1; 7.1.1; 11.2; 11.3 |
Wide distribution in the world. However, in Brazil, it is restricted to the mountains of the state of RJ with EOO of 17,414 km² and AOO of 12,000 km². In addition, it presents many subpopulations in high-altitude fields of the INP. Despite being within protected areas, the species is subject to decline in EOO, AOO and habitat quality due to frequent fires in the regions of occurrence. |
Pottiaceae |
*Leptodontium stellatifolium (Hampe) Broth. |
VU |
VU |
B1ab(iii)+2ab(iii) |
1.1; 2.1; 6.1; 7.1.1; 8.1; 8.2.1; 11.2; 11.3 |
Neotropical distribution. In Brazil it is restricted to the Atlantic Forest (ES, MG, RJ, SP and SC). It has an EOO of 8,235,581 km² and an AOO of 48,000km². The species and its region of occurrence suffer threats from urban activities such as real estate expansion, implementation of agricultural activities, excessive tourism, presence of provoked fire and introduction of exotic species that cause a decline in the quality and extension of the habitat. It was recently collected from exposed rock and rocky outcrops. |
Pottiaceae |
*Leptodontium wallisii (Müll.Hal.) Kindb. |
VU |
VU |
B1ab(i,ii,iii) |
6.1; 7.1.1; 11.2; 11.3 |
Disjunct between South America and Africa. In Brazil, the species occurs in rain forests and high-altitude fields in the states of SP and RJ (EOO=12,534.519 km²), and it may possibly occur in the state of MG. Despite being within protected areas, the species is subject to decline in EOO, AOO and habitat quality due to frequent fires and excessive tourism in the regions of occurrence. |
Polytrichaceae |
*Notoligotrichum minimum (Cardot) G.L.Sm. |
NE |
EN |
B1ab(i,ii,iii) |
6.1; 7.1.1; 11.2; 11.3 |
Disjunct between Tierra del Fuego (Argentina) and RJ state. In Brazil, the species is restricted to the INP. With an AOO of 12,000 km², it has small isolated subpopulations. The species is subject to decline in EOO, AOO and habitat quality due to frequent fires and excessive tourism in the region of occurrence. |
Rhabdoweisiaceae |
*Oreoweisia brasiliensis Hampe
|
VU |
CR |
B1ab(iii)+B2ab(iii) |
6.1; 7.1.1; 11.2; 11.3 |
Rare species, with disjunct occurrence between the Andes and INP. It has an AOO of 8,000 km². The populations are restricted to the trail to Agulhas Negras. It faces the decline in the quality and extension of the habitat due to the presence of fire and excessive tourism in the region. |
Polytrichaceae |
*Pogonatum perichaetiale subsp. oligodus (Müll. Hal.) Hyvönen
|
VU |
EN |
B2ab(ii,iii, iv) |
6.1; 7.1.1; 11.2; 11.3 |
This species is widely distributed in the Neotropics and Africa. In the American continent, it occurs in Central and South America (Hyvönen 1989Hyvönen J. 1989. A synopsis of genus Pogonatum (Polytrichaceae, Musci). Acta Botanica Fennica 138: 1-87. ). In Brazil, it occurs in the high-altitude fields of Serra da Mantiqueira in the states of Minas Gerais and Rio de Janeiro (Peralta 2009Peralta DF. 2009. Polytrichaceae (Polytrichales, Bryophyta) do Brasil. PhD Thesis, Instituto de Pesquisas Ambientais, Brazil. ). It occurs in montane forests and high-altitude fields only in the area limited by the Atlantic Forest. This species normally grows on hummus between rock fissures in places directly exposed to the sun. It presents AOO of 12.000 km², due to the species presenting microhabitat specificity and facing the decline in habitat quality and extension due to frequent fires in the region and excessive tourism, it allows evaluating the species as EN. |
Sematophyllaceae |
*Sematophyllum swartzii (Schwägr.)W.H.Welch & H.A. Crum
|
VU |
LC |
|
|
This species have a Neotropical distribution. Widely distributed in the Atlantic Forest, occurring in rainforest and high-altitude fields. It presents many recent collection records. |
Splachnaceae |
Tetraplodon mnioides Müll.Hal.
|
VU |
CR |
B1ab(i, ii, iii)+B2ab(i, ii, iii) |
6.1; 7.1.1; 11.2; 11.3 |
Costa et al. (2005Costa DP, Imbassahy CAA, Silva VPAV. 2005. Diversidade e Importância das Espécies de Briófitas na Conservação dos Ecossistemas do Estado do Rio de Janeiro. Rodriguésia 56: 13-49.) considered T. itatiaiae Müll.Hal. as VU. However, the material was taxonomically revised, is considered a synonym of T. mnioides. Despite being well distributed in the northern hemisphere, in Brazil it is rare, restricted to the high-altitude fields of the INP. It has an AOO of 8,000 km². It is known from only one location, suffering from declining habitat quality. Individuals of the Splachnaceae family present dispersion mediated by flies and grow on animal dung, which may constitute a rarity factor for the species, since it has few collections, collection efforts and investments in scientific research are necessary in order to certify the real geographic distribution of the species and its ecology. |
Calliergonaceae |
*Warnstorfia exannulata (Schimp.) Loeske
|
VU |
CR |
B1b(i,ii,iii,iv) + B1c(i,ii,iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species has a wide distribution in the northern hemisphere. In South America it is restricted to tropical mountains. In Brazil, the species is restricted to the INP high-altitude fields with AOO< 8,000 km². The population is restricted to the region of the source of the Campo Belo River. It faces a decline in habitat quality and extension, due to the presence of fire and excessive tourism in the region. |
|
Endemic to Brazil |
|
|
|
|
|
Bartramiaceae |
*Breutelia microdonta (Mitt.) Broth. |
NE |
LC |
|
|
This species is endemic and widely distributed in the Atlantic Forest (RJ, ES, MG, SP, SC and PR), found in rainforest and high-altitude fields. With EOO of 41,129 km². Throughout its distribution, it is found in protected areas. |
Bartramiaceae |
*Breutelia wainioi Broth. |
NE |
LC |
|
|
This species is endemic and widely distributed in the Atlantic Forest (RJ, MG, RS) with an EOO of 63,674 km². Throughout its distribution, it is found in protected areas. |
Dicranaeceae |
*Campylopus fragilis ssp. fragiliformis (J.-P.Frahm) J.-P.Frahm |
NE |
DD |
|
|
As it is a subspecies, herbarium collections need to be reviewed. |
Dicranaceae |
Campylopus gemmatus (Müll.Hal.) Paris |
NE |
LC |
|
|
This species is endemic to Brazil, widely distributed throughout the country, occurs in the Cerrado and Atlantic Forest, with an EOO of 757,647,600 km². Along its distribution it is found in protected areas. |
Ditrichaceae |
*Cladastomum ulei Müll.Hal. |
NE |
VU |
B1ab(i,ii,iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to the Atlantic Forest of southeastern Brazil with EOO of 1,022 km² and AOO of 20,000 km². Restricted to the high-altitude fields of the INP and the Parque Nacional do Caparaó (ES). It faces a decline in the quality and extension of the habitat, due to the presence of fire and excessive tourism in the regions of occurrence. |
Ephemeraceae |
*Ephemerum pachyneuron Müll.Hal. |
NE |
CR |
B1b(i,ii,iii,iv) + B1c(i,ii,iii) |
6.1; 7.1.1; 11.2; 11.3 |
This species is endemic to the INP, with records only for the Pedra do Altar trail. It has AOO< 4,000 km². In addition, it has an annual life strategy and occurs on hummus. It faces a decline in the quality and extension of the habitat, due to the presence of fire and excessive tourism in the regions of occurrence. Only a recent collection (2020), was found in the same previously recorded location, Pedra do Altar. |
Polytrichaceae |
*Itatiella ulei (Broth. ex Müll.Hal.) G.L.Sm. |
NE |
NT |
|
|
This species is endemic to Brazil, with an EOO of 35,759 km² in the southeast region. It has records in the following Protected areas: Caparaó National Park (MG, ES), INP (MG, RJ), Serra dos Órgãos National Park (RJ), Campos do Jordão State Park (SP), Ibitipoca State Park (MG) (Yano & Peralta 2011Yano O, Peralta DF. 2011. Flora da Serra do Cipó, Minas Gerais: Briófitas (Anthocerotophyta, Bryophyta e Marchantiophyta). Boletim de Botânica 29: 135-211.). Furthermore, the species is restricted to upper montane forests and high-altitude fields. It may be included in some threat category in the near future due to the species occurring in regions that suffer from urbanization, presence of fire and excessive tourism. |
Polytrichaceae |
*Polytrichum angustifolium Mitt. |
NE |
LC |
|
|
This species is endemic to the Atlantic Forest, with a wide distribution, EOO of 117,152.538km², occurring in the states of ES, MG, PR, RJ, RS, SC, SP (Peralta 2009Peralta DF. 2009. Polytrichaceae (Polytrichales, Bryophyta) do Brasil. PhD Thesis, Instituto de Pesquisas Ambientais, Brazil. ). It has records in the following Protected areas throughout its distribution: Caparaó National Park, Pedra Azul Forest Reserve, Nova Lombardia Biological Reserve, INP, Serra dos Órgãos National Park, Desengano State Park, Campos de Jordão State Park, among others (Peralta 2009Peralta DF. 2009. Polytrichaceae (Polytrichales, Bryophyta) do Brasil. PhD Thesis, Instituto de Pesquisas Ambientais, Brazil. ). |
Rhacocarpaceae |
*Rhacocarpus inermis (Müll.Hal.) Lindb. |
NE |
LC |
|
|
This species is endemic and widely distributed in the Atlantic Forest, occurring in the states of RJ, MG, ES, SC and RS with EOO 110,237.324 km². In addition, the species occurs within the boundaries of several Protected areas throughout its range (CNCFlora 2012CNCFlora. 2012. Rhacocarpus inermis in Lista Vermelha da flora brasileira. Centro Nacional de Conservação da Flora. http://cncflora.jbrj.gov.br/portal/pt-br/profile/Rhacocarpus inermis. 27 sep. 2023. http://cncflora.jbrj.gov.br/portal/pt-br...
). |
Sphagnaceae |
Sphagnum perforatum Warnst. |
NE |
VU |
B2ab(ii, iii) |
5.2; 5.2.1; 11.2; 11.3 |
This species is endemic to the Atlantic Forest (RJ, MG, SP, PR), with an EOO of 51,135.844 km² and a reduced AOO (16,000 km²). Species restricted to high montane forests and high-altitude fields. It presents threats arising from extractivism and commercial harvesting, since, in general, they are not cultivated, but extracted directly from nature to meet the demands of the floriculture sector (Rancura et al. 2010Rancura S, Ribeiro MM, Nordi N. 2010. Considerações sobre a coleta de Sphagnum no município de Cananéia, estado de São Paulo, Brasil. Acta Botanica Brasilica 24: 328-334. ; Negrelle et al. 2014Negrelle RRB, Bordignon SE, Ferreira MR, Sampaio LK. 2014. Extrativismo e comercialização de Sphagnum (veludo): Características, implicações socioeconômicas e ecológicas e perspectivas. Revista Brasileira de Horticultura Ornamental 20: 53-66.; Glime 2007Glime JM. 2007. Bryophyte Ecology. Vol. I Physiological Ecology. Michigan Technological University and the International Association of Bryologists. https://digitalcommons.mtu.edu/bryophyte-ecology/. 17 Set. 2023. https://digitalcommons.mtu.edu/bryophyte...
). And it is poorly represented in scientific collections. |