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First record of Histiotus diaphanopterus Feijó, Rocha & Althoff, 2015 (Chiroptera, Vespertilionidae) in the state of Tocantins, Brazil

Gentil, Mariane de Almeida; Hofmann, Gabriel Selbach; Coelho, Igor Pfeifer; Cordeiro, José Luís Passos; Brito de Oliveira, Marcione

Abstract

We report the first record of Histiotus diaphanopterus Feijó, Rocha & Althoff, 2015 in the state of Tocantins, Brazil and the third record of the species in the Cerrado biome, reinforcing its association with seasonally dry environments of the South American diagonal of open formations. Morphological traits confirm specimen identity, with transparent wings as the most distinctive diagnostic character. Our findings highlight the species’ ecological specificity and exposure to anthropogenic threats, including habitat loss and climate change, underscoring the need for further studies and integrated conservation strategies.

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the journal of biodiversity data NOTES ON GEOGRAPHIC DISTRIBUTION 1143 Academic editor: Roberto Leonan Novaes Received: 8 September 2025 Accepted: 13 November 2025 Published: 24 November 2025 Copyright © The authors. This is an open‑access article distributed under terms of the Creative Commons Attribution License (Attribution 4.0 International – CC BY 4.0) Abstract. We report the first record of Histiotus diaphanopterus Feijó, Rocha & Althoff, 2015 in the state of Tocantins, Brazil and the third record of the species in the Cerrado biome, reinforcing its association with seasonally dry environments of the South American diagonal of open formations. Morphological traits confirm specimen identity, with transparent wings as the most distinctive diagnostic character. Our findings highlight the species’ ecological specificity and exposure to anthropogenic threats, including habitat loss and climate change, underscoring the need for further studies and integrated conservation strategies. Key words. Cerrado biome, global biodiversity hotspots, Neotropical Savanna, range extension, South America, transparent wings Gentil MA, Hofmann GS, Coelho IP, Cordeiro JLP, de Oliveira MB (2025) First record of Histiotus diaphanopterus Feijó, Rocha & Althoff, 2015 (Chiroptera, Vespertilionidae) in the state of Tocantins, Brazil. Check List 21 (6): 1143–1152. https://doi.org/10.15560/21.6.1143 Introduction The family Vespertilionidae currently comprises 545 species arranged into 62 genera and four subfamilies: Vespertilioninae, Kerivoulinae, Murininae, and Myotinae (Simmons and Cirranello 2025). Nine vespertilionid genera occur in the Neotropics: Bauerus Van Gelder, 1959, Corynorhinus H. Allen, 1865, Eptesicus Rafinesque, 1820, Histiotus Gervais, 1856, Lasiurus Gray, 1831, Myotis Kaup, 1829, Neoeptesicus Cláudio et al., 2023, Perimyotis Menu, 1984, and Rhogeessa H. Allen, 1866 (Wilson and Reeder 2005; Gardner 2007; Cláudio et al. 2023). Histiotus is currently represented by 11 species (Simmons and Cirranello 2025), all endemic to South America and broadly distributed across the continent, from northern Venezuela to the southern regions of Chile and Argentina. Its range extends from western Venezuela and Colombia southward through Ecuador, Peru, and Bolivia to Paraguay and northwestern Argentina (Wilson and Reeder 2005; Gardner 2007; Cláudio et al. 2023). Five species are known to occur in Brazil (Garbino et al. 2024): Histiotus alienus Thomas, 1916, H. diaphanopterus Feijó, Rocha & Althoff, 2015, H. laephotis Thomas, 1916, H. montanus (Philippi & Landbeck, 1861), and H. velatus (I. Geoffroy, 1824). These species are broadly distributed except for the Amazon, with records from the Northeastern, across the Central-Western, to the Southeastern and Southern regions, reaching as far as the state of Rio Grande do Sul (Gardner 2007; Cláudio et al. 2023). Species of this genus are medium-sized to large bats characterized by a distinctive combination of morphological traits, including long ears connected by a band of skin with variable development; skull is delicate, narrow, and long; sagittal and lambdoidal crests weakly developed; postorbital process of the jugal well developed; and usually long dorsal fur (Reis et al. 2017; Cláudio et al. 2023). 21 (6) · https://doi.org/10.15560/21.6.1143 21 (6): 1143–1152. https://doi.org/10.15560/21.6.1143 First record of Histiotus diaphanopterus Feijó, Rocha & Althoff, 2015 (Chiroptera, Vespertilionidae) in the state of Tocantins, Brazil Mariane de Almeida Gentil1, 2 , Gabriel Selbach Hofmann3, Igor Pfeifer Coelho4, José Luís Passos Cordeiro3, 5 , MarcioneBritode Oliveira2, 6 1 Instituto de Biociências, Universidade Federal do Estado do Rio de Janeiro, Rio de Janeiro, RJ, Brazil 2 Setor de Mastozoologia, Departamento de Vertebrados, Museu Nacional, Universidade Federal do Rio de Janeiro, Rio de Janeiro, RJ, Brazil 3 International Platform for Science, Technology and Innovation in Health (PICTIS), Aveiro, Portugal 4 Independent Researcher, Florianópolis, SC, Brazil 5 Instituto Oswaldo Cruz, Fundação Oswaldo Cruz, Eusébio, CE, Brazil 6 Laboratório de Biologia e Parasitologia de Mamíferos Silvestres Reservatórios, Instituto Oswaldo Cruz, Fundação Oswaldo Cruz, Rio de Janeiro, RJ, Brazil Corresponding author: Marcione B. de Oliveira (oliveira01mar[email protected]) Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1144 Histiotus species are rarely captured in the field and are poorly represented in scientific collections. For instance, in the Mammal Collection of the Museu Nacional at Universidade Federal do Rio de Janeiro, Brazil, there are only 32 specimens of the genus, of which 28 are cataloged, including a single specimen of H. diaphanopterus documented in the present study. Consequently, Histiotus remains one of the least-known genera of Neotropical bats, although recent studies have revealed the existence of new species within the genus (Feijó et al. 2015; Rodríguez-Posada et al. 2021; Velazco et al. 2021). Histiotus diaphanopterus was described by Feijó et al. (2015), with the type locality in Boqueirão da Onça, municipality of Sento Sé, state of Bahia, within the Brazilian Caatinga. In the same study, the species was also reported from four additional localities, three in the Caatinga and Cerrado biomes of Brazil, including the states of Paraíba (São José dos Cordeiros), Ceará (Fortaleza), and Maranhão (Tasso Fragoso); and one in the Chaco ecoregion of Bolivia, department of Santa Cruz (Pampagrande). The distribution of the species was later expanded with new records in the Cerrado biome from the state of Mato Grosso (Cuiabá) and with additional records in the Chaco ecoregion of Santa Cruz, Bolivia (Valle Grande; Semedo and Feijó 2016). Recently, the species was reported from the state of Pernambuco, with records from two municipalities, Buíque and Tupanatinga, within the Caatinga biome (Bernard et al. 2023). Here, we report a range extension of H. diaphanopterus to Tocantins, representing the third record of the species in the Cerrado biome of Brazil. We also provide an updated distribution map and a table summarizing external and cranial measurements for all known specimens. Figure 1. Records of Histiotus diaphanopterus in Brazil and Bolivia (see also Table 1). This study: 1 = Tocantins, Lizarda; Literature records: 2 = Bahia, Sento Sé, Boqueirão da Onça (type locality), 3 = Ceará, Fortaleza, Faculdade Veterinária do Ceará, 4 = Maranhão, Tasso Fragoso, Tranqueira, 5 = Mato Grosso, Cuiabá, Chapada dos Guimarães, Escola Evangélica Burit, 6 = Paraíba, São José dos Cordeiros, Reserva Particular do Patrimônio Natural Fazenda Almas, 7 = Pernambuco, Buíque, Parque Nacional do Catimbau, 8 = Pernambuco, Tupanatinga, Parque Nacional do Catimbau, 9 = Santa Cruz, Valle Grande, Potrerillos, and 10 = Santa Cruz, Pampagrande, Florida. Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1145 Study area The new record of H. diaphanopterus was made in the Lizarda municipality, Tocantins, Brazil (Figure 1). This region has a tropical climate with a dry winter (Aw type on the Köppen classification), characteristic of tropical savannas (Peel et al. 2007). The vegetation corresponds to Cerrado rupestre, a phytophysiognomy associated with rocky outcrops of quartzite–arenite (Ribeiro and Walter 1998). This environment is characterized by shallow, stony soils with low nutrient availability and high acidity, resulting in restrictive edaphic conditions for vegetation development. The vegetation cover is predominantly herbaceous-shrubby, sparse and discontinuous, interspersed with small woody species adapted to nutrient-poor substrates and seasonal drought. Such areas harbor a specialized flora, with high levels of endemism and functional traits that enhance resilience to fire and soil limitations (Ribeiro and Walter 1998). Methods In April 2019, we installed two sampling sets of five mist nets: one within the vegetation in front of a quartz–arenite rocky formation, approximately 120 m from the outcrop, and the other along an abandoned road about 100 m from the first set. Nets were opened at sunset and remained active for six hours. Inspections were carried out every 20 minutes. All captured specimens were placed in individual holding bags and field annotations included forearm length, body mass, sex, and reproductive condition. Preliminary identification was conducted in the field using taxonomic keys (Reis et al. 2017). We measured the specimens in the laboratory using digital calipers (0.01 mm of precision) according to Feijó et al. (2015) and Semedo and Feijó (2016; Table 2). External measurements: weight (W), total length (TL), head–body length (HBL), tail length (T), hind-foot length (HF), ear length (E), height of skin between ears (HSE), forearm length (FA), tragus length (Tr), calcar length (CaL), ear breadth (EB). Cranial measurements: greatest length of skull (GLS), condyloincisive length (CIL), postorbital constriction (PC), zygomatic breadth (ZB), braincase breadth (BB), mastoid breadth (MB), height of postorbital process (HPP), palatal length (PL), maxillary toothrow length (C-M³), palatal breadth (PB), breadth across M3–M3 (M³-M³), breadth across canines (C-C), mandible length (ML), mandibular toothrow length (C-M₃), mandible height (MH). Results Histiotus diaphanopterus Feijó, Rocha & Althoff, 2015 Figures 2, 3 New records. BRAZIL – Tocantins • Lizarda municipality; −9.5733, −46.8104; 362 m a.s.l.; 22.IV.2019; de Oliveira MB; 1 adult ♀, MN84764. Table 1. Geographic records of Histiotus diaphanopterus in Brazil and Bolivia, including country, state/department, locality, coordinates, associated vegetation domain, and references. The new record from Tocantins (present study) represents the northernmost occurrence of the species in the Cerrado biome. No. = number relative to the locations in Figure 1. No. Country State / department Locality Latitude Longitude Vegetation Reference 1Brazil Tocantins Lizarda −9.5733 −46.8104 Cerrado Present study 2Brazil Bahia Sento Sé, Boqueirão da Onça −9.8803 −41.0709 Caatinga Feijó et al. 2015; ICMBio 2025 3Brazil Ceará Fortaleza, Faculdade Veterinária do Ceará −3.7860 −38.5525 Caatinga Feijó et al. 2015; ICMBio 2025 4Brazil Maranhão Tasso Fragoso, Tranqueira −8.4725 −45.7428 Cerrado Feijó et al. 2015; ICMBio 2025 5Brazil Mato Grosso Cuiabá, Chapada dos Guimarães, Escola Evangélica Buriti −15.4156 −55.8071 Cerrado Semedo and Feijó 2016; ICMBio 2025 6 Brazil Paraíba São José dos Cordeiros, Reserva Particular Patrimônio Natural Fazenda Almas −7.4708 −36.8975 Caatinga Feijó et al. 2015; ICMBio 2025 7 Brazil Pernambuco Buíque, Parque Nacional do Catimbau −8.4791 −37.2369 Caatinga Bernard et al. 2023; ICMBio 2025 8Brazil Pernambuco Tupanatinga, Parque Nacional do Catimbau −8.4282 −37.3096 Caatinga Bernard et al. 2023; ICMBio 2025 9 Bolivia Santa Cruz Valle Grande, Potrerillos −18.5500 −64.9333 Chaco Semedo and Feijó 2016; Poma-Urey et al. 2023 10 Bolivia Santa Cruz Pampagrande, Florida −17.9297 −64.1633 Chaco Feijó et al. 2015; Poma−Urey et al. 2023 Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1146 Identification. The specimen weighs 8 g, with a head–body length of 110.86 mm, tail length 50.95 mm, forearm length 46.74 mm, and ear length 28.01 mm (Table 2). The ears are conspicuously large, translucent, connected by a high band across the forehead (4.62 mm), and with the tragus extending to about half their height (Figure 3A, C). Wings and uropatagium are translucent and well developed, with the tail slightly exceeding the distal margin of the uropatagium (Figure 3B, C). The dorsal fur is long (9.5 mm) and distinctly bicolored, with dorsal dark brown hairs at the base and golden at the tips, and ventral dark brown fur at the base with whitish tips (Figure 3B, C). Cranially, the inner upper incisors are widely spaced; the outer incisors are small, in contact with the inner incisors and slightly separated from the canines. The upper M³ is narrow, about half the width of M¹ and M² (Figure 2). Dental formula: i: 2/3; c: 1/1; pm: 1/2; m: 3/3 = 32. Comparison. Comparison with H. velatus, which occurs in Brazil and may also be present in the study region. Histiotus diaphanopterus and H. velatus are the most similar species within the genus, sharing a triangular ear (fine and acute) with a prominent inner lobe connected by a band across the forehead. However, they differ in a combination of external and cranial traits. Histiotus diaphanopterus exhibits well-defined bicolor hairs on the dorsum (with hairs tipped in pale), whereas H. velatus tends to have a subtly bicolored dorsum. The wing membranes of H. diaphanopterus are pale and translucent (similar to those of H. laephotis) in contrast to the darker membranes of H. velatus. Cranial and body measurements further support their distinction. Although the overall skull shape is similar, H. diaphanopterus Figure 2. Dorsal, ventral, and lateral views of the skull and mandible of Histiotus diaphanopterus (MN84764). Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1147 is generally smaller than H. velatus in several dimensions, including total body and tail length, skull length, braincase width, mastoid width, width across M³, and mandibular length. In the examined specimen, the combination of translucent wings, conspicuously bicolored dorsum, proportionally narrower M³, and longer ventral fur supports its identification as H. diaphanopterus. When compared with other species occurring in Brazil but outside the study area, H. laephotis also has translucent wings but differs in pelage pattern (subtly bicolored dorsum) and in auricular (oval in shape) and cranial features. Histiotus montanus and H. alienus generally have darker pelage and wings, whereas the analyzed specimen is distinguished by its bicolored dorsum and translucent membranes. Moreover, these species tend to have a more oval ear morphology compared to H. diaphanopterus. The combination of transparent wings, bicolored fur, large ears connected by a high band, and reduced M³ width distinguishes the specimen from all other Histiotus. Figure 3. Histiotus diaphanopterus (MN84764). A. Lateral view showing conspicuously large ears. B. General golden-brown fur with distinctly bicolored dorsal hairs (dark brown at the base and golden at the tips) and translucent uropatagium. C. Translucent ears and wings. Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1148 Literature records. The distribution of H. diaphanopterus includes Brazil and Bolivia. In Brazil, there are records from the northeast (Bahia, Ceará, Maranhão, Paraíba, and Pernambuco) and the west (Mato Grosso). The type locality is in Brazil, in the state of Bahia, in Sento Sé municipality, at Boqueirão da Onça. In Bolivia, the department of Santa Cruz (Table 1). Moreover, the species occurs in the Caatinga, Cerrado, and Chaco ecoregions. Ecological note on roost use and interactions. Roost sharing by H. diaphanopterus and Molossus sp., and a potential interaction between these bat species and an insect of the family Reduviidae, since an individual was observed in the same roost. Both bat species were observed in this vertical cavity within a quartz–arenite rocky formation (Figure 4), approximately 2 m above the ground, the roost measured approximately 6 cm in width, 25 cm in length, and 20 cm in depth. Discussion Histiotus diaphanopterus has been recorded from only 10 localities to date, occurring across the Caatinga, Cerrado, and Chaco ecoregions (Feijó et al. 2015; Semedo and Feijó 2016; Bernard et al. 2023). The record reported here extends the known geographic range of the species by approximately 170 km from the nearest locality in the State of Maranhão, within the Cerrado biome, now totaling three known localities in this biome (Figure 1, locality 4), and about 630 km from the type locality in the Caatinga biome (Figure 1, locality 2). Additionally, we increase the number of bat species recorded for the state of Tocantins to 87 (Souza et al. 2021). When compared with the 2024 mammal checklist published by the Sociedade Brasileira de Mastozoologia (Abreu et al. 2024), Tocantins ranks sixth in bat species richness, tied with Amapá. However, some of the values in that checklist may be outdated, since the species richness reported for Tocantins is considerably lower than that documented by Souza et al. (2021). The specimen reported in this study, as well as those previously documented in the literature, was found in a region characterized by alternating wet and dry seasons, a climatic pattern typical of the Cerrado, Caatinga, and Chaco (Peel et al. 2007). These three ecoregions, where the species occurs, share ecological and climatic similarities and are often described as part of the South American diagonal of open formations (Werneck 2011). All are defined by pronounced climatic seasonality, with prolonged dry periods that shape vegetation adapted to water scarcity, heterogeneous habitat mosaics, Table 2. External and cranial measurements (in mm) and body mass (g) of Histiotus diaphanopterus specimens examined in this study and from the literature. Specimens are represented by voucher MN84764 from Lizarda, Tocantins; UPFB 9490–9500 from Sento Sé, Bahia; UFPB 6014 and UFPB 6015 from São José dos Cordeiros, Paraíba; UFMT 2751 from Chapada dos Guimarães, Mato Grosso, Brazil; MNKM 3714 and AMNH 264086 from Valle Grande, Santa Cruz, Bolivia. Sex: female (♀) and male (♂). Museu Nacional, Universidade Federal do Rio de Janeiro (MN), Brazil; Universidade Federal da Paraíba (UFPB), Brazil; Universidade Federal de Mato Grosso (UFMT), Brazil; Museo Noel Kempff Mercado (MNKM), Bolivia; American Museum of Natural History (AMNH), USA. Abbreviations of measurements are explained in Methods. MN 84764 UPFB 9490* UPFB 9491 UPFB 9492 UPFB 9493 UPFB 9494 UPFB 9495 UPFB 9496 UPFB 9497 UPFB 9498 UPFB 9499 UPFB 9500 UFPB 6015 UFPB 6014 MNKM 3714 UFMT 2751 AMNH 264086 Sex ♀♀♂♀♀♂♀♂♀♀♂♀♀♀♀♀♀ W 8.00 10.00 8.50 9.50 9.00 8.00 − 8.00 11.00 10.00 8.00 8.50 10.50 9.00 9.00 − 10.90 TL 110.86 104.60 100.60 111.80 111.00 108.30 105.00 104.00 114.80 103.60 105.50 106.60 113.00 104.00 − − 121.00 HBL 59.91 53.20 52.60 56.50 60.00 54.80 58.80 52.00 60.20 52.40 53.20 56.20 − 52.90 60.00 − − T50.95 51.40 48.00 55.3 51.00 53.50 46.20 52.00 54.60 51.20 52.20 50.40 43.00 52.00 57.00 − 57 HF 9.64 10.10 10.00 7.90 9.30 8.00 10.90 8.10 8.40 10.50 9.30 10.10 8.00 7.60 8.00 − 8.00 E 28.01 31.40 33.10 32.10 30.40 30.30 31.40 28.80 31.70 29.90 30.90 30.60 29.30 28.20 27.00 − 31.00 HSE 4.62 4.00 − − − 3.90 4.50 − 4.40 3.40 3.80 − − − − − − FA 46.74 44.90 44.60 45.40 46.80 43.90 44.70 41.80 47.20 45.30 44.40 45.70 46.60 45.30 46.00 45.40 Tr 13.62 13.50 12.90 13.50 13.80 13.30 13.00 13.20 13.20 13.00 14.10 13.50 14.70 13.10 − − 17.00 CaL 17.86 17.70 18.90 17.20 17.20 23.30 17.50 17.90 17.70 20.30 17.80 20.10 − − − − − EB 19.92 21.30 21.30 − 21.70 22.80 20.80 18.50 20.50 20.10 21.40 20.40 − − − − − GLS 17.53 18.63 18.08 18.12 18.31 17.80 17.90 17.67 18.30 − 17.50 17.50 18.00 − − 17.44 − CIL 17.22 17.13 16.79 17.01 17.11 16.44 16.95 16.34 17.10 16.90 16.30 16.30 16.60 − − 16.91 17.17 PC 3.73 4.05 4.05 4.06 3.87 4.00 3.73 3.86 4.00 3.90 4.10 3.85 4.25 − − 3.89 3.79 ZB − 10.65 10.00 10.29 10.34 10.04 9.90 10.06 10.26 9.90 10.10 10.00 10.41 − − 10.48 10.43 BB 7.50 7.85 8.05 7.73 7.64 7.64 7.48 7.68 7.84 7.70 7.60 7.46 8.00 − − 7.96 7.67 MB 8.20 6.96 7.04 6.95 6.86 6.60 6.90 6.62 7.10 6.90 6.40 6.55 7.22 − − 8.11 6.35 HPP 2.19 2.05 1.76 02.01 2.00 1.96 1.90 1.76 1.82 2.02 2.40 1.90 2.38 − − 1.89 1.76 PL 7.61 7.64 7.61 7.65 7.70 7.22 7.55 7.26 7.56 7.60 7.10 7.40 8.33 − − 7.37 7.68 C-M³ 5.95 6.21 5.84 6.10 6.27 5.90 6.05 5.82 6.08 5.80 5.80 5.75 5.93 − − 6.19 6.16 PB 3.77 3.61 3.33 3.26 3.31 3.36 2.96 3.28 3.16 3.10 3.00 3.42 3.09 − − 3.70 3.41 M³-M³ 6.38 6.89 6.23 6.4 6.18 6.30 6.22 6.32 6.62 6.40 6.10 6.18 6.46 − − 6.77 6.52 C-C 4.98 5.20 4.81 4.92 − 4.60 4.67 4.73 5.14 4.70 4.80 4.68 4.78 − − 5.16 4.91 ML 12.12 12.70 12.30 12.35 12.55 11.85 12.54 11.72 12.36 12.70 12.00 12.05 12.57 − − 12.28 12.42 C-M₃ 6.29 6.63 5.95 6.18 6.18 6.16 6.35 6.31 6.57 6.20 6.10 6.23 6.39 − − 6.53 6.64 MH 3.97 4.46 3.85 4.20 4.20 4.16 4.36 4.08 4.32 4.10 4.00 4.04 4.20 − − 5.45 4.40 Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1149 and high diversity of species specialized in arid environments (Werneck 2011; Fernandes et al. 2022). Within this system, the Cerrado biome plays a central role as a major source of floristic exchanges with neighboring ecoregions, notably the Caatinga, which represents the most species-rich nucleus of the Seasonally Dry Tropical Forests and has received substantial contributions from Cerrado lineages (Fernandes et al. 2022). Although connectivity with the Chaco has historically been more limited, all three ecoregions share diversification processes linked to global aridification since the Miocene, which fostered the evolution of drought-adapted faunas and floras (Carmignotto et al. 2012; Fernandes et al. 2022). From a faunal perspective, the Cerrado biome exhibits the highest mammalian richness and a high proportion of endemic species, followed by the Caatinga and then the Chaco, while both Caatinga and Chaco display relatively low levels of endemism, supporting their inclusion within a broader complex of interconnected open landscapes (Klink and Machado 2005; de Albuquerque et al. 2012; Abreu et al. 2024). Based on current records, H. diaphanopterus is the only species of the genus restricted to tropical regions with dry and shrubby vegetation (Feijó et al. 2015; Semedo and Feijó 2016; Bernard et al. 2023; Poma-Urey et al. 2023). The other species that occur in Brazil, H. alienus, H. laephotis, H. montanus, and H. velatus, are associated with the Atlantic Forest, whereas H. velatus is also recorded in the Caatinga, Cerrado, and Pampa biomes (ICMBio 2025). Ultimately, morphological variation in H. diaphanopterus appears to be subtle, and the species can be readily distinguished from its congeners based on the traits described by Feijó et al. (2015), most notably its transparent wings. Most recorded measurements are consistent with the expected range for the species, with only minor variations. The height of skin between the ears and the mastoid breadth were slightly higher than the average observed in other individuals of the same species. In addition, our observation of H. diaphanopterus and Molossus sp. sharing a roost with an insect of the family Reduviidae suggests a potential ecological interaction between bats and reduviids. Although our observation is occasional, similar associations have been reported in the literature. Some reduviFigure 4. Area where voucher specimen MN84764 was collected. A. Rupestrian cerrado with quartzite–sandstone outcrops in the background. B. Colony of Histiotus diaphanopterus in a quartzite–sandstone outcrop at Lizarda, Tocantins, Brazil. The arrows black indicates (A) the roost location and (B) the insect belonging to the family Reduviidae. Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1150 ids found in bat roosts are species that may act as predators associated with guano deposits, contributing to the regulation of invertebrate populations and highlighting the complexity of guano-based food webs (Ferreira and Martins 1999). More recent studies based on fossil records preserved in Dominican amber have revealed one of the oldest known associations between a triatomine bug and a trypanosome, as well as the presence of bat hairs within the same specimens, indicating that bats may have served as vertebrate hosts for Trypanosoma parasites millions of years ago (Poinar 2005). Together, these findings underscore the ecological complexity of bat roost communities and suggest that interactions between bats and reduviids may range from ancient parasitic relationships to contemporary trophic associations. However, as a recently described species with only scattered occurrence records, consistent information remains lacking regarding key aspects of its biology, including diet and population structure. Moreover, similar to the ecoregions it inhabits, the Caatinga, Cerrado, and Chaco, H. diaphanopterus faces threats from human activities, such as agricultural expansion, deforestation, and fire, which lead to habitat fragmentation and biodiversity loss (Werneck 2011; de Albuquerque et al. 2012). Historically, these regions have received less scientific and conservation attention compared to humid biomes such as the Amazon and the Atlantic Forest, further increasing the vulnerability of their native species (Werneck 2011; de Albuquerque et al. 2012). Climate change exacerbates these threats through rising temperatures, reduced rainfall, and the expansion and intensification of the dry season (Hofmann et al. 2021, 2023), exerting additional pressure on populations. In addition, the species is listed as Least Concern in the Brazilian List of Threatened Species (ICMBio 2025). However, there are few known records, and it has not yet been assessed by the International Union for Conservation of Nature (IUCN 2025). Taken together, these factors highlight the urgent need for comprehensive studies on H. diaphanopterus and for integrated conservation strategies that consider both the shared evolutionary history of these open biomes and the critical role of their species in maintaining continental biodiversity. Acknowledgements We thank Dr. Luiz Flamarion B. de Oliveira for his contributions to the development of the manuscript and Rodrigo C. Dutra for his assistance in editing the skull figure. We thank the reviewers and editors for their contributions, which improved this work. Additional information Conflict of interest The authors declare that no competing interests exist. Ethical statement All procedures were conducted under authorization from the ‘Sistema de Autorização e Informação em Biodiversidade’ (SISBIO/ICMBio), permit No. 60058, and approved by the Animal Ethics Committee (CEUA/UFRJ), protocol No. 016/21. Funding Field sampling was funded by ‘Fundação de Amparo à Pesquisa do Estado de São Paulo’ (FAPESP; grant 2017/22269-2). Marcione B. de Oliveira received support from the ‘Fundação de Amparo à Pesquisa do Estado do Rio de Janeiro’ (FAPERJ; grant E-26/200.022/2024). Author contributions Conceptualization: MBO, MAG. Data curation: MBO, MAG. Investigation: MBO, MAG, GSH, IPC, JLPC. Methodology: MBO, MAG. Supervision: MBO. Visualization: MBO, MAG. Writing – original draft: MBO, MAG. Writing – review and editing: MBO, MAG, GSH, IPC, JLPC. Author ORCID iDs Mariane de Almeida Gentil https://orcid.org/0009-0007-2850-0014 Gabriel Selbach Hofmann https://orcid.org/0000-0003-2525-8537 Igor Pfeifer Coelho https://orcid.org/0000-0003-3645-9094 José Luís Passos Cordeiro https://orcid.org/0000-0001-5821-8764 Marcione Brito de Oliveira https://orcid.org/0000-0003-1628-3458 Data availability All data that support the findings of this study are available in the main text. Check List 21 (6) · https://doi.org/10.15560/21.6.1143 Gentil et al. · Histiotus diaphanopterus in Tocantins 1151 References Abreu EF, Casali D, Costa-Araújo R, Garbino GST, Libardi GS, Loretto D, Loss AC, Marmontel M, Moras LM, Nascimento MC, Oliveira ML, Pavan SE, Tirelli FP (2024) Lista de Mamíferos do Brasil (2024-1). Zenodo. https:// doi.org/10.5281/zenodo.14536925 Bernard E, Barbier ES, Leal ESB, Santos FI, Pimentel NT, Pereira JSB, Hintze FSO, Bezerra JDP, Motta CMS (2023) Morcegos no Parque Nacional do Catimbau, Pernambuco, Brasil: síntese de uma década (2012–2022) de pesquisas. Biodiversidade Brasileira 13 (2): 1–17. https://doi.org/10.37002/biobrasil.v13i2.2384 Carmignotto AP, de Vivo M, Langguth A (2012) Mammals of the Cerrado and Caatinga: distribution patterns of the tropical open biomes of Central South America. In: Patterson BD, Costa LP (Eds.) Bones, clones and biomes: the history and geography of recent Neotropical mammals. University of Chicago Press, Chicago, USA, 307–350. Cláudio VC, Novaes RLM, Gardner AL, Nogueira MR, Wilson DE, Maldonado JE, Oliveira JA, Moratelli R (2023) Taxonomic re-evaluation of New World Eptesicus and Histiotus (Chiroptera: Vespertilionidae), with the description of a new genus. Zoologia (Curitiba) 40: e22029. https://doi.org/10.1590/S1984-4689.v40.e22029 de Albuquerque UP, Araújo EL, El-Deir ACA, Lima ALA, Souto A, Bezerra BM, Ferraz EMN, Freire EMX, Sampaio EVS, Las-Casas FMG, Moura GJB, Pereira GA, Melo JG, Ramos MA, Rodal MJN, Schiel N, Lyra-Neves RM, Alves RRN, Azevedo-Júnior SM, Telino-Júnior WR, Severi W (2012) Caatinga revisited: ecology and conservation of an important seasonal dry forest. The Scientific World Journal 2012: 205182. https://doi. org/10.1100/2012/205182 Feijó A, Rocha PA, Althoff SL (2015) New species of Histiotus (Chiroptera: Vespertilionidae) from northeastern Brazil. Zootaxa 4048 (3): 412–427. https://doi.org/10.11646/zootaxa.4048.3.4 Fernandes MF, Cardoso D, Pennington RT, de Queiroz LP (2022) The origins and historical assembly of the Brazilian Caatinga Seasonally Dry Tropical Forests. Frontiers in Ecology and Evolution 10: 723286. https://doi. org/10.3389/fevo.2022.723286 Garbino GST, Gregorin R, Lima IP, Loureiro L, Moras L, Moratelli R, Nogueira MR, Pavan AC, Tavares VC, Nascimento MC, Novaes RLM, Peracchi AL (2024) Updated checklist of Brazilian bats: versão 2024. Comitê da Lista de Morcegos do Brasil—CLMB, Sociedade Brasileira para o Estudo de Quirópteros (Sbeq). Available at: https:// www.sbeq.org.br/lista-especies. Accessed on: 2025-08-19. Gardner AL (2007) [2008] Mammals of South America. Volume 1. University of Chicago Press, Chicago, USA, 690 pp. Hofmann GS, Cardoso MF, Alves RJ, Weber EJ, Barbosa AA, de Toledo PM, de Oliveira LF (2021) The Brazilian Cerrado is becoming hotter and drier. Global Change Biology 27 (17): 4060–4073. https://doi.org/10.1111/gcb. 15712 Hofmann GS, Silva RC, Weber EJ, Barbosa AA, Oliveira LFB, Alves RJV, Hasenack H, Schossler V, Aquino FE, Cardoso MF (2023) Changes in atmospheric circulation and evapotranspiration are reducing rainfall in the Brazilian Cerrado. Scientific Reports 13: 11236. https://doi.org/10.1038/s41598-023-38174-x ICMBio (2025) Sistema de Avaliação do Risco de Extinção da Biodiversidade – SALVE. Available at: https://salve.ic mbio.gov.br/. Accessed on: 2025-07-12. IUCN (2025) The IUCN Red List of Threatened Species. Version 2025-2. Available at: https://www.iucnredlist.org. Accessed on: 2025-11-05. Klink CA, Machado RB (2005) A conservação do Cerrado brasileiro.Megadiversidade1 (1): 147–155. Peel MC, Finlayson BL, McMahon TA (2007) Updated world map of the Köppen-Geiger climate classification. Hydrology and Earth System Sciences 11 (5): 1633–1644. https://doi.org/10.5194/hess-11-1633-2007 Poma-Urey JL, Acosta SLH, Rivero K, Hidalgo-Cossio M, Hingst-Zaher E, Gualda-Barros J, da Natividade BD, Barboza-Marquez K, Ramírez-Chaves HE, Salazar-Bravo J, Ochoa JG (2023) Taxonomic revision and additional comments of some bats (Mammalia, Chiroptera) reported from Bolivia, with an updated checklist based on voucher material with verified identities. Check List 19 (3): 409–427. https://doi.org/10.15560/19.3.409 Reis NR, Peracchi AL, Batista CB, Lima IP, Pereira AD (2017) História natural dos morcegos brasileiros: chave de identificação de espécies. Technical Books Editora, Rio de Janeiro, Brazil, 416 pp. Ribeiro JF, Walter BMT (1998) Fitofisionomias do bioma Cerrado. In: Sano SM, Almeida SP (Eds.) Cerrado: ambiente e flora. EMBRAPA-CPAC, Planaltina, Brazil, 89–166. Rodríguez-Posada ME, Morales-Martínez DM, Ramírez-Chaves HE, Martínez-Medina D, Calderón-Acevedo CA (2021) A new species of long-eared brown bat of the genus Histiotus (Chiroptera) and the revalidation of Histiotus colombiae. Caldasia 43 (2): 221–234. https://doi.org/10.15446/caldasia.v43n2.85424 Semedo TBF, Feijó A (2016) Filling the gap: first record of the Transparent-winged Big-eared Bat Histiotus diaphanopterus (Chiroptera: Vespertilionidae) in southwestern Brazil. Mammalia 81 (3): 323–327. https://doi.org/10. 1515/mammalia-2016-0043 Simmons NB, Cirranello AL (2025) Bat species of the world: a taxonomic and geographic database. Version 1.8.1. https://batnames.org. Accessed on: 2025-08-22. Souza MB, Santos CGA, Silva GAFQ, Alves APS, Assis RA, Santos LRS, Borges RE, Pacheco SM (2021) Morcegos do Tocantins: lista de verificação de espécies. Revista Ibero Americana de Ciências Ambientais 12 (11): 55–64. https://doi.org/10.6008/CBPC2179-6858.2021.011.0006 Velazco PM, Almeida FC, Cláudio VC, Giménez AL, Giannini NP (2021) A new species of Histiotus Gervais, 1856 (Chiroptera, Vespertilionidae), from the Pacific coast of northern Peru. American Museum Novitates 2021