“…We obtained anuran richness data from the following checklists conducted in 28 protected areas ( Figure 3): Caatinga (12 protected areas) -Catimbau National Park -CatNP, state of Pernambuco (Pedrosa et al 2014), Seridó Ecological Station -SerES, state of Rio Grande do Norte (Caldas et al 2016), Delta do Parnaíba Environmental Protection Area -DPEPA, states of Maranhão and Piauí (Loebmann & Mai 2008, Andrade et al 2016, Araújo et al 2018, Serra das Confusões National Park -SCoNP and Uruçuí-Una Ecological Station -UUES, both in state of Piauí (Dal Vechio et al 2013, Lençóis Maranhenses National Park -LMNP, state of Maranhão (Miranda 2007), Chapada do Araripe Environmental Protection Area -ChpEPA, Ubajara National Park -UbaNP and Aiuaba Ecological Station -AuES, state of Ceará (Ribeiro et al 2012, Costa et al 2018, Castro et al 2019, Chapada Diamantina National Park -CDNP and Raso da Catarina Ecological Station -RcatES, state of Bahia (Garda et al 2013, Magalhães et al 2015 Bertoluci 2007, Bertoluci et al 2009), Serra da Bodoquena National Park -SrBNP, state of Mato Grosso do Sul (Uetanabaro et al 2007), Assis Ecological Station -AsES, Jataí Ecological Station -JatES, Furnas de Bom Jesus State Park -FurSP, and Itirapina Ecological Station -ItiES, state of São Paulo (Brasileiro et al 2005, Araujo et al 2009, Prado et al 2009 We evaluate anuran species distribution and association with Brazilian biomes (IBGE 2019) from literature records (i.e. Roberto et al 2013, Andrade et al 2017, Araújo et al 2018, Frost 2020) and the amphibian conservation status is according to IUCN (2020). All diversity metrics and similarity analysis were performed using the packages adespatial (Dray et al 2019), BiodiversityR (Kindt and Coe 2005), and Vegan (Oksanen et al 2016) for R 5.6.1 (R Core Team 2019).…”