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Addressing biodiversity knowledge shortfalls in New World Helicopsychidae (Insecta, Trichoptera): Potential distribution, environmental gradients, and identification of conservation and research priority areas

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acknowledge that our data are limited by current knowledge of species distribution, and future research may expand the distribution range of species. Distribution patterns and potential distribution in New World The initial step in addressing the challenges posed by BKS is the compilation of inventories, checklists, descriptions of new species, and new distribution records [36]. However, it is equally important to consider other aspects, such as ecology, biology, phenology, and ethology, which can inform biodiversity conservation policies and the consequences of anthropogenic interventions (e.g., climate change, suppression of riparian vegetation) [23,25,26,71]. This study estab- lishes the environmental gradients for the H. (Feropsyche) and H. (Cochliopsyche) species. Despite the considerable range of elevation, temperature, and precipitation observed across both subgenera, the data indicated a higher prev- alence of H. (Feropsyche) species in coastal areas of tropical and temperate environments, across a wide elevation gradient (0–5042 m a.s.l.), in low order streams and in areas with high rainfall (Figs 3 and 4). On the other hand, the H. (Cochliopsyche) species are restricted to tropical environments, with prevalence in rainforests and lowland areas. Of the distributional records, 55% are in higher order streams (>4th order) (Figs 3 and 4). The results presented here concur with previous hypotheses proposed by Monson et al. [72], Flint [62,63], and Johan-

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son [41,45]. However, this study provides a comprehensive overview of the distribution and analyzes the differences in environmental space between the subgenera. In addition to the morphological differences, these factors contribute to the accumulation of divergence between the NW Helicopsychidae lineages. Currently, there is still no clear resolution regard- ing their phylogenetic relationship. Some hypotheses suggest that they are sister groups [73], while others posit that they are distant clades [30], further complicating their taxonomic placement. Despite its wide distribution in tropical regions, H. (Cochliopsyche) is largely restricted to the type locality or adjacent localities (S1 Table). Distribution records are scarce and generally consist of single collections with a small number of specimens (S1 Table). This is primarily due to the greater concentration of collection and research efforts on Trichoptera in small, oxygenated freshwater environments, where most of the group’s diversity is concentrated [34]. It is therefore rec- ommended that research efforts be directed towards the at inventorying of South America’s large rivers, with priority areas for H. (Cochliopsyche) studies (areas of high suitability and low research effort) including all South America’s large river basins (e.g., Amazon, Orinoco, Paraná, and São Francisco River basins), with a particular focus on the large size rivers (Fig 1C). The species of H. (Feropsyche) are distributed across a wide range of habitats, from the temperate areas of the

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Nearctic Region to the Andean areas of Chile (Fig 1E). However, the areas with the highest environmental suitability are throughout Central America (including the Antilles), the Florida Keys, areas east of the Andes between Argentina and

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PLOS One | https://doi.org/10.1371/journal.pone.0327580 July 28, 2025 18 / 22 Bolivia (Chaco domain), and the coastal region of northwest and east South America. Much of continental Central Amer- ica, the Antilles, and the northwest of South America have been well sampled (Fig 1D). However, areas of the Chaco domain, the northern portion and Central Corridor of Atlantic Forest, and high-altitude areas of the Cerrado and Caatinga domains remain poorly sampled (Fig 1E). These areas should be prioritized for research efforts, in agreement with the Brazilian caddisfly studies of Santos et al. [24], which indicated the to prioritize research efforts in the Northeastern and Central-Western regions of Brazil. The Patagonian subregion is one of the least researched in the NT, with both groups exhibiting low suitability for this region. However, 11 species of H. (Feropsyche) are found in areas with minimum temperatures below 0°C (e.g., H. (Fer- opsyche) borealis, −17°C; H. (Feropsyche) minuscula, −12°C) (Fig 1D). The data available do not permit us to determine whether the low suitability is (i) due to the absence of favorable environmental conditions, or (ii) to the scarcity of data, which resulted in the model’s limitation for this area. In general, there is a considerable range of distribution records for the Helicopsyche in the NW. The species are distributed across a wide environmental gradient, with H. (Feropsyche) being particularly notable for their ability to occur in various freshwater environments across the New World. This includes a wide range of altitudes,

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temperatures, and precipitation levels, with a preference for low-order environments (Figs 1,3, and 4). In contrast, H. (Cochliopsyche) species typically occur in lowlands, environments with higher average temperatures, and a preference for large rivers, reflecting a restriction in their occurrence to large river basins (Figs 1,3, and 4). Thus, the results indicate that the two lineages have specialized in different niches: H. (Feropsyche) specialized in smaller (low-order) environments, while the H. (Cochliopsyche) specialized in larger (high-order) environments. Similar patterns are also observed in other Trichoptera lineages, including Hydrobiosidae (Amphichorema and Atopsyche), and Glossosomatidae (Culoptila and Cariboptila) [33]. The results of this study highlight critical conservation implications for Helicopsychidae species in the New World. The identification of environmental gradients and the discovery of species with restricted distribution in high-suitability and low research effort areas emphasize the need for targeted conservation efforts. Areas with high species richness and environ- mental suitability, such as parts of Central and South America, should be prioritized for further research and protection. The underexplored regions, especially tropical rainforests and the dry diagonal zones (Caatinga, Cerrado, and Chaco), represent significant gaps in knowledge and potential hotspots for biodiversity. Increasing faunistic surveys in these regions will not

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only enhance species descriptions but also help mitigate the risk of extinction for species with narrow distribution ranges, which are more susceptible to threats such as climate change and habitat loss. Moreover, the conservation of riparian habitats, particularly in large river basins, is critical to maintaining the integrity of ecosystems supporting these specialized species. By addressing both Linnean, Wallacean, Haeckelian, and Hutchinsonian and other shortfalls, future research can refine conservation strategies and promote the preservation of these important freshwater ecosystems. Conclusion The results highlight recent progress in the taxonomy and distributional cataloguing of New World Helicopsychidae, partic- ularly within underexplored regions of the Neotropics. Despite a substantial increase in described species, significant gaps in biodiversity knowledge remain. Current estimates suggest that up to 75% of Helicopsyche species in the region are still undescribed, emphasizing the urgent need for continued research efforts—ideally incorporating all semaphoronts—to fully document and understand the diversity of NW Helicopsychidae The distribution of Helicopsyche species reveals complex patterns influenced by environmental factors such as ele- vation, temperature, and precipitation. Species of H. (Cochliopsyche) are typically associated with larger river systems in warmer climates and extensive river basins, whereas H. (Feropsyche) species show broader ecological tolerance,

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occurring across diverse freshwater habitats throughout the Americas, particularly in low-order streams. These contrasting patterns reflect distinct ecological specializations between the two subgenera.

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PLOS One | https://doi.org/10.1371/journal.pone.0327580 July 28, 2025 19 / 22 Sampling efforts across the New World remain uneven, with the majority of data derived from historically surveyed regions (e.g., the Antilles) or areas with established research institutions (e.g., Central America, the Amazon, and the Atlantic Forest). These regions, due to their high species richness, should be prioritized in conservation planning, especially those identified as biodiversity hotspots. However, vast areas remain poorly explored, including the Amazon lowlands, northern and central Atlantic Forest, high-altitude environments in the Caatinga and Cerrado domains, and tran- sitional zones between major phytogeographic domains. Targeted research in these underrepresented areas is essential. This study represents a foundational step toward a more comprehensive database of Trichoptera diversity in the New World. It provides critical tools for delineating biogeographic patterns and identifying knowledge gaps, thereby enhancing our understanding of Helicopsychidae diversity. The compilation presented herein establishes a valuable baseline for future taxonomic, ecological, and conservation-oriented studies on this family. and may inspire future research proposals for this family or other Trichoptera taxa using similar approaches. Supporting information S1 Table. Summary of georeferenced distribution data for all New World Helicopsychidae species. (XLSX) S2 Table. Summary of distribution in Freshwater Ecoregion (sensu Abell et al. 2015) and limits data for biogeocli-

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matic variables of all New World Helicopsychidae species. (XLSX) S3 Table. Pearson correlation between environmental variables. (XLSX) S1 Fig. Boxplot with the result of Pearson correlation between environmental variables. (TIFF) S2 Fig. Boxplot with result of evaluation of distribution modelling algorithms using the area under curve (AUC) method. (TIF) Acknowledgments We extend our sincere thanks to Dr. Neusa Hamada, Dr. Ana Maria Pês, and Dr. Gleison R. Desidério for kindly providing data and permitting the analysis of material from the Laboratório de Citotaxonomia e Insetos Aquáticos of the Instituto Nacional de Pesquisas da Amazônia (LACIA-INPA). We are also grateful to the Museum of Comparative Zoology (MCZ) at Harvard and to Dr. Crystal A. Maier for granting access to, and assisting with the analysis of, biological material from the MCZ collection. Our appreciation further extends to Dr. Ralph Holzenthal and Dr. Robin E. Thomson at the University of Minnesota, and to Dr. Dikow Torsten of the Smithsonian Institution for kindly loaning specimens from institutional collec- tions for analysis at the MCZ. Author contributions Conceptualization: Rafael Pereira, Adolfo Calor. Data curation: Rafael Pereira. Formal analysis: Rafael Pereira. Funding acquisition: Adolfo Calor.

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PLOS One | https://doi.org/10.1371/journal.pone.0327580 July 28, 2025 20 / 22 Investigation: Rafael Pereira. Methodology: Rafael Pereira. Resources: Adolfo Calor. Supervision: Adolfo Calor. Validation: Rafael Pereira. Visualization: Rafael Pereira. Writing – original draft: Rafael Pereira. Writing – review & editing: Adolfo Calor. References 1. Droissart V, Dauby G, Hardy OJ, Deblauwe V, Harris DJ, Janssens S, et al. Beyond trees: biogeographical regionalization of tropical Africa. J Bio- geogr. 2018;45(5):1153–67. https://doi.org/10.1111/jbi.13190 2. Kreft H, Jetz W. A framework for delineating biogeographical regions based on species distributions. J Biogeogr. 2010;37(11):2029–53. https://doi. org/10.1111/j.1365-2699.2010.02375.x 3. Oliveira U, Paglia AP, Brescovit AD, de Carvalho CJB, Silva DP, Rezende DT, et al. The strong influence of collection bias on biodiversity knowl- edge shortfalls of Brazilian terrestrial biodiversity. Divers Distribut. 2016;22(12):1232–44. https://doi.org/10.1111/ddi.12489 4. Vogel Ely C, de Bordignon SAL, Trevisan R, Boldrini II. Implications of poor taxonomy in conservation. J Nat Conserv. 2017;36:10–3. https://doi. org/10.1016/j.jnc.2017.01.003 5. Kier G, Mutke J, Dinerstein E, Ricketts TH, Küper W, Kreft H, et al. Global patterns of plant diversity and floristic knowledge. J Biogeogr. 2005;32(7):1107–16. https://doi.org/10.1111/j.1365-2699.2005.01272.x 6. Collen B, Ram M, Zamin T, McRae L. The Tropical biodiversity data gap: addressing disparity in global monitoring. Trop Conserv Sci.

Trang 20 · Đoạn 51Vị trí nguồn

2008;1(2):75–88. https://doi.org/10.1177/194008290800100202 7. Yang W, Ma K, Kreft H. Geographical sampling bias in a large distributional database and its effects on species richness–environment models. J Biogeogr. 2013;40(8):1415–26. https://doi.org/10.1111/jbi.12108 8. Hortal J, de Bello F, Diniz-Filho JAF, Lewinsohn TM, Lobo JM, Ladle RJ. Seven shortfalls that beset large-scale knowledge of biodiversity. Annu Rev Ecol Evol Syst. 2015;46(1):523–49. https://doi.org/10.1146/annurev-ecolsys-112414-054400 9. Faria L, Pie M, Salles F, Soares E. The Haeckelian shortfall or the tale of the missing semaphoronts. J Zool Syst Evol Res. 2020;59(2):359–69. https://doi.org/10.1111/jzs.12435 10. Tessarolo G, Ladle RJ, Lobo JM, Rangel TF, Hortal J. Using maps of biogeographical ignorance to reveal the uncertainty in distributional data hidden in species distribution models. Ecography. 2021;44(12):1743–55. https://doi.org/10.1111/ecog.05793 11. Terribile LC, Feitosa DT, Pires MG, de Almeida PCR, de Oliveira G, Diniz-Filho JAF, et al. Reducing Wallacean shortfalls for the coralsnakes of the Micrurus lemniscatus species complex: present and future distributions under a changing climate. PLoS One. 2018;13(11):e0205164. https://doi. org/10.1371/journal.pone.0205164 PMID: 30427853 12. Ceballos G, Ehrlich PR, Dirzo R. Biological annihilation via the ongoing sixth mass extinction signaled by vertebrate population losses and declines. Proc Natl Acad Sci U S A. 2017;114(30):E6089–96. https://doi.org/10.1073/pnas.1704949114 PMID: 28696295

Trang 20 · Đoạn 52Vị trí nguồn

13. Montoya JM, Donohue I, Pimm SL. Planetary gradients for biodiversity: implausible science, pernicious policies. Trends Ecol Evol. 2018;33(2):71– 3. https://doi.org/10.1016/j.tree.2017.10.004 14. Strayer DL, Dudgeon D. Freshwater biodiversity conservation: recent progress and future challenges. J North Am Benthol Soc. 2010;29(1):344–58. https://doi.org/10.1899/08-171.1 15. Watson JEM, Evans T, Venter O, Williams B, Tulloch A, Stewart C, et al. The exceptional value of intact forest ecosystems. Nat Ecol Evol. 2018;2(4):599–610. https://doi.org/10.1038/s41559-018-0490-x PMID: 29483681 16. Tickner D, Opperman JJ, Abell R, Acreman M, Arthington AH, Bunn SE, et al. Bending the curve of global freshwater biodiversity loss: an emer- gency recovery plan. Bioscience. 2020;70(4):330–42. https://doi.org/10.1093/biosci/biaa002 PMID: 32284631 17. Harper M, Mejbel HS, Longert D, Abell R, Beard TD, Bennett JR, et al. Twenty‐five essential research questions to inform the protection and resto- ration of freshwater biodiversity. Aquat Conserv: Mar Freshw Ecosyst. 2021;31(9):2632–53. https://doi.org/10.1002/aqc.3634 18. Morse JC . Biodiversity of aquatic insects. Insect Biodiversity Science and Society. 2017;1:205–227. https://doi.org/10.1002/9781118945568 19. Morse JC, Frandsen PB, Graf W, Thomas JA. Diversity and ecosystem services of Trichoptera. Insects. 2019;10(5):125. https://doi.org/10.3390/ insects10050125 PMID: 31052441

Trang 21 · Đoạn 53Vị trí nguồn

PLOS One | https://doi.org/10.1371/journal.pone.0327580 July 28, 2025 21 / 22 20. de Moor FC, Ivanov VD. Global diversity of caddisflies (Trichoptera: Insecta) in freshwater. Hydrobiologia. 2007;595(1):393–407. https://doi. org/10.1007/s10750-007-9113-2 21. Thomas JA, Frandsen PB, Prendini E, Zhou X, Holzenthal RW. A multigene phylogeny and timeline for Trichoptera (Insecta). Syst Entomol. 2020;45(3):670–86. https://doi.org/10.1111/syen.12422 22. Thomas JA, Frandsen PB, Morse JC. Revised chronology of Trichoptera evolution. Contribut Entomol. 2023;73(2):289–94. https://doi.org/10.3897/ contrib.entomol.73.e110405 23. Ríos-Touma B, Holzenthal RW, Huisman J, Thomson R, Rázuri-Gonzales E. Diversity and distribution of the Caddisflies (Insecta: Trichoptera) of Ecuador. PeerJ. 2017;5:e2851. https://doi.org/10.7717/peerj.2851 PMID: 28097062 24. Santos APM, Dumas LL, Henriques-Oliveira AL, Souza WRM, Camargos LM, Calor AR, et al. Taxonomic Catalog of the Brazilian Fauna: order Trichoptera (Insecta), diversity and distribution. Zoologia. 2020;37:1–13. https://doi.org/10.3897/zoologia.37.e46392 25. Ríos-Touma B, Cuesta F, Rázuri-Gonzales E, Holzenthal R, Tapia A, Calderón-Loor M. Elevational biodiversity gradients in the Neotropics: Per- spectives from freshwater caddisflies (Insecta: Trichoptera). PLoS One. 2022;17(8):e0272229. https://doi.org/10.1371/journal.pone.0272229 PMID: 35930543 26. Razo-González M, Novelo-Gutiérrez R, Castaño-Meneses G, Márquez J. Diversity and composition of Caddisflies (Insecta: Trichoptera) along an

Trang 21 · Đoạn 54Vị trí nguồn

elevation gradient in southeastern Mexico. Diversity. 2023;15(1):110. https://doi.org/10.3390/d15010110 27. Harvey BJ. Emergent hotspots of biotic disturbances and their consequences for forest resilience. Front Ecol Environ. 2023;21(8):388–96. 28. Kusch J. Interacting influences of climate factors and land cover types on the distribution of caddisflies (Trichoptera) in streams of a central Euro- pean low mountain range. Insect Conserv Diversity. 2014;8(1):92–101. https://doi.org/10.1111/icad.12088 29. Sánchez-Bayo F, Wyckhuys KAG. Worldwide decline of the entomofauna: a review of its drivers. Biol Conserv. 2019;232:8–27. https://doi. org/10.1016/j.biocon.2019.01.020 30. Johanson KA. Phylogenetic and biogeographic analysis of the family Helicopsychidae (Insecta: Trichoptera). Entomol Scandinav Suppl. 1998;53:1–172. 31. Morse JC. Trichoptera World Checklist. 2024 [cited 24 Sep 2024]. http://entweb.clemson.edu/database/trichopt/index.htm 32. Pereira R, Calor AR. Helicopsyche (Feropsyche) Johanson, 1998 (Trichoptera) from Northeastern Mata Atlântica Freshwater ecoregion: integrating taxonomy and niche modeling. An Acad Bras Cienc. 2024;96(1):e20230369. https://doi.org/10.1590/0001-3765202420230369 PMID: 38808813 33. Holzenthal RW, Calor AR. Catalog of the neotropical Trichoptera (Caddisflies). Zookeys. 2017;(654):1–566. https://doi.org/10.3897/zook- eys.654.9516 PMID: 28331396 34. Holzenthal RW, Thomson RE, Ríos-Touma B. Order Trichoptera. In: Thorp JH, Covich AP, editors. Thorp and Covich’s Freshwater Invertebrates.

Trang 21 · Đoạn 55Vị trí nguồn

Academic Press; 2015. pp. 965–1002. https://doi.org/10.1016/b978-0-12-385026-3.00038-3 35. Johanson KA. Zoogeography and diversity of the snail case caddisflies (Trichoptera: Helicopsychidae). In: Holzenthal RW, Flint OS, editors. Pro- ceedings of the 8th International Symposium on Trichoptera. Columbus, Ohio: Ohio Biological Survey; 1997. pp. 205–12. 36. Calor AR, Pereira R, Queiroz LL, Vilarino A, de Azevedo Junior CCD, Queiroz A, et al. LEAq – Laboratório de Entomologia Aquática “Prof. Clau- dio Gilberto Froehlich” and the task of facing the biodiversity knowledge deficits on Caddisflies (Trichoptera), Bahia, Brazil. Rev Bras entomol. 2023;67(spe). https://doi.org/10.1590/1806-9665-rbent-2023-0065 37. Dumas LL, Nessimian JL. New species of Helicopsyche von Siebold 1856 (Trichoptera: Helicopsychidae) from Brazil, including the redescription of Helicopsyche (Feropsyche) planorboides Machado 1957. Zootaxa. 2019;4619(2). https://doi.org/10.11646/zootaxa.4619.2.2 PMID: 31716301 38. Neto JDLG, Ribeiro JMF, Passos MAB. Two new species of Helicopsyche Siebold 1856 (Insecta: Trichoptera: Helicopsychidae) from Pará State, northern Brazil. Zootaxa. 2019;4565(3). https://doi.org/10.11646/zootaxa.4565.3.8 PMID: 31716468 39. Cavalcante-Silva A, Pereira R, Calor AR. Caddisflies (Trichoptera) checklist and a new species of Helicopsyche von Siebold, 1856, from the Brejo de Altitude de Triunfo, a relict rainforest within the Caatinga domain, Northeast Brazil. Zookeys. 2022;1111:215–44. https://doi.org/10.3897/zook- eys.1111.77541 PMID: 36760847

Trang 21 · Đoạn 56Vị trí nguồn

40. Moreno L, Desidério GR, Pes AM, Hamada N. Two New Species of Helicopsyche (Feropsyche) Johanson (Trichoptera: Helicopsychidae) from Central Amazon, Brazil. Ann Entomol Soc Am. 2023;73(1). https://doi.org/10.3161/00034541anz2023.73.1.003 41. Johanson KA. Revision of the Neotropical caddisfly subgenus Helicopsyche (Cochliopsyche) (Trichoptera, Helicopsychidae), with descriptions of twelve new species. Insect Syst Evol. 2003;34(4):381–414. https://doi.org/10.1163/187631203x00036 42. de Souza WRM, Lima LRC, Pes AMO, Pinheiro U. Trichoptera (Insecta) from Pernambuco State, northeastern Brazil. J Nat History. 2013;47(45– 46):2905–14. https://doi.org/10.1080/00222933.2013.791948 43. Desiderio GR, Santana V, Pereira ES, Pes AM, Hamada N. On the Identity of Smicridea (Smicridea) aequalis Banks, 1920 (Trichoptera: Hydro- psychidae): morphology of adults and immature stages, bionomics, distribution, and male color dimorphism. Neotrop Entomol. 2021;50(3):430–43. https://doi.org/10.1007/s13744-021-00860-8 PMID: 33740226 44. Razo-González M, Novelo-Gutiérrez R, Castaño-Meneses G, Márquez J. Checklist of the caddisflies (Insecta: Trichoptera) from Oaxaca, Mexico. Rev Mex Biodiv. 2023;94:e945275. https://doi.org/10.22201/ib.20078706e.2023.94.5275 45. Johanson KA. Systematic revision of American Helicopsyche of subgenus Feropsyche (Trichoptera: Helicopsychidae). Insect Syst Evol. 2002;60:1–151.

Trang 22 · Đoạn 57Vị trí nguồn

PLOS One | https://doi.org/10.1371/journal.pone.0327580 July 28, 2025 22 / 22 46. .Pes AM, Holzenthal RW, Sganga JV, Santos APM, Barcelos-Silva P, Camargos LM. Order Trichoptera. In: Hamada N, Thorp JD, Rogers C, editors. Thorp and Covich’s Freshwater Invertebrates. 4th ed. Vol. 3. San Diego: Academic Press; 2018. pp. 237–324. https://doi.org/10.1016/ b978-0-12-804223-6.00010-x 47. Larsson M, Göthberg A, Milberg P. Night, light and flight: light attraction in Trichoptera. Insect Conserv Diver. 2019;13(3):296–302. https://doi. org/10.1111/icad.12379 48. Morrone JJ. Biogeographical regionalisation of the Neotropical region. Zootaxa. 2014;3782:1–110. https://doi.org/10.11646/zootaxa.3782.1.1 PMID: 24871951 49. Morrone JJ, Escalante T, Rodríguez-Tapia G, Carmona A, Arana M, Mercado-Gómez JD. Biogeographic regionalization of the neotropical region: New map and shapefile. An Acad Bras Cienc. 2022;94(1):e20211167. https://doi.org/10.1590/0001-3765202220211167 PMID: 35107518 50. Escalante T, Rodrguez-Tapia G, Morrone JJ. Toward a biogeographic regionalization of the Nearctic region: area nomenclature and digital map. Zootaxa. 2021;5027(3):351–75. https://doi.org/10.11646/zootaxa.5027.3.3 PMID: 34811166 51. Vinson MR, Hawkins CP. Broad‐scale geographical patterns in local stream insect genera richness. Ecography. 2003;26(6):751–67. https://doi. org/10.1111/j.0906-7590.2003.03397.x 52. Oksanen J, et al. Vegan: Community Ecology Package. 2019. Avialble from: from: https://cran.r-project.org/web/packages/vegan

Trang 22 · Đoạn 58Vị trí nguồn

53. Kindt R, Coe R. Tree diversity analysis: A manual and software for common statistical methods for ecological and biodiversity studies. Nairobi: World Agroforestry Centre (ICRAF); 2005. 54. Palmer MW. The estimation of species richness by extrapolation. Ecology. 1990;71(3):1195–8. https://doi.org/10.2307/1937387 55. Hortal J, Borges PAV, Gaspar C. Evaluating the performance of species richness estimators: sensitivity to sample grain size. J Anim Ecol. 2006;75(1):274–87. https://doi.org/10.1111/j.1365-2656.2006.01048.x PMID: 16903065 56. Nix HA. A biogeographic analysis of Australian elapid snakes. Atlas of Elapid Snakes of Australia. Canberra: Australian Gov. Publ. Service; 1986. 57. Carpenter G, Gillison AN, Winter J. DOMAIN: a flexible modelling procedure for mapping potential distributions of plants and animals. Biodivers Conserv. 1993;2(6):667–80. https://doi.org/10.1007/bf00051966 58. Nelder JA, Wedderburn RWM. Generalized linear models. J R Stat Soc Series A (General). 1972;135(3):370. https://doi.org/10.2307/2344614 59. Tax DMJ, Duin RPW. Support vector data description. Mach Learn. 2004;54(1):45–66. https://doi.org/10.1023/b:mach.0000008084.60811.49 60. VanDerWal J, Shoo LP, Graham C, Williams SE. Selecting pseudo-absence data for presence-only distribution modeling: How far should you stray from what you know?. Ecol Modell. 2009;220(4):589–94. https://doi.org/10.1016/j.ecolmodel.2008.11.010 61. Hanley JA, McNeil BJ. The meaning and use of the area under a receiver operating characteristic (ROC) curve. Radiology. 1982;143:29–36.

Trang 22 · Đoạn 59Vị trí nguồn

62. Flint OS. Studies of neotropical caddisflies, XIV: On a collection from northern Argentina. Proc Biol Soc Washington. 1972;85:223–48. 63. Flint OS. Studies of neotropical caddisflies, XXXIII: new species from austral South America (Trichoptera). Smithsonian Contrib Zool. 1983;377:1–98. 64. Flint OSJ. Studies of neotropical caddisflies, XXXVI. The genus Cochliopsyche in middle America (Trichoptera: Helicopsychidae). Anales del Insti- tuto de Biología, Universidad Nacional Autónoma de México, Series de Zoología. 1986;56:213–6. 65. Oláh J, Oláh J Jr. New Neotropical Trichoptera: Banyallarga and Phylloicus species delineation by revisited paraproct (Calamoceratidae). Opusc Zool. 2022;53(2):205–25. https://doi.org/10.18348/opzool.2022.2.205 66. Abell R, Thieme ML, Revenga C, Bryer M, Kottelat M, Bogutskaya N, et al. Freshwater ecoregions of the world: a new map of biogeographic units for freshwater biodiversity conservation. BioScience. 2008;58(5):403–14. https://doi.org/10.1641/b580507 67. Rasmussen AK, Morse JC. Distributional checklist of Nearctic Trichoptera (2022 revision). Tallahassee: Florida A&M University. 2024. [cited 5 Sep 2024]. Available from: http://www.Trichoptera.org 68. Martín PAR, Miranda ÁVI. Association of immature stages of some caddisfly species from northwestern Argentina with description of a new species of Helicopsyche (Trichoptera: Helicopsychidae). Zootaxa. 2015;3949(2):203–16. https://doi.org/10.11646/zootaxa.3949.2.3 PMID: 25947802

Trang 22 · Đoạn 60Vị trí nguồn

69. Johanson KA. A catalog of the Helicopsychidae (Insecta: Trichoptera) of the world. Bull Zool Museum. 1995;14:101–23. 70. Bueno-Soria J. Five new species of caddisflies (Trichoptera) from Mexico. Proc Entomol Soc Washington. 1983;85:450–5. 71. Múrria C, Sáinz‐Bariáin M, Vogler AP, Viza A, González M, Zamora‐Muñoz C. Vulnerability to climate change for two endemic high‐elevation, low‐ dispersive Annitella species (Trichoptera) in Sierra Nevada, the southernmost high mountain in Europe. Insect Conserv Diversity. 2019;13(3):283– 95. https://doi.org/10.1111/icad.12387 72. Monson MP, Holzenthal RW, Ahlstrand GG. The Larva and Pupa of Cochliopsyche vazquezae (Trichoptera:Helicopsychidae). J North Am Benthol Soc. 1988;7(2):152–9. https://doi.org/10.2307/1467920 73. Johanson KA, Malm T, Espeland M. Molecular phylogeny of Sericostomatoidea (Trichoptera) with the establishment of three new families. Syst Entomol. 2016;42(1):240–66. https://doi.org/10.1111/syen.12209