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Map showing the range of eastern red bats and all sampling locations. Only labeled locations (black dots) had sufficient sample sizes to be included in population-level analyses, and labels reflect two-letter state or province codes (two sampling locations within West Virginia are further labeled with the first two letters of the county to distinguish them). The range map source is the IUCN (http://www. iucnredlist.org/details/11347/0): Arroyo-Cabrales J, Miller B, Reid F, CuarónCuar´Cuarón AD, de Grammont PC. 2008. Lasiurus borealis. In IUCN 2014. IUCN Red List of Threatened Species. Version 2014.2. <www. iucnredlist.org>. Downloaded on November 5, 2013.

Map showing the range of eastern red bats and all sampling locations. Only labeled locations (black dots) had sufficient sample sizes to be included in population-level analyses, and labels reflect two-letter state or province codes (two sampling locations within West Virginia are further labeled with the first two letters of the county to distinguish them). The range map source is the IUCN (http://www. iucnredlist.org/details/11347/0): Arroyo-Cabrales J, Miller B, Reid F, CuarónCuar´Cuarón AD, de Grammont PC. 2008. Lasiurus borealis. In IUCN 2014. IUCN Red List of Threatened Species. Version 2014.2. <www. iucnredlist.org>. Downloaded on November 5, 2013.

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Article
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Documented fatalities of bats at wind turbines have raised serious concerns about the future impacts of increased wind power development on populations of migratory bat species. However, for most bat species we have no knowledge of the size of populations and their demographic trends, the degree of structuring into discrete subpopulations, and whet...

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Context 1
... of the population (that portion contributing genes to the next generation). Further, regular monitoring of N e might serve as a proxy for tracking changes in population size over Table 1 Sites sampled and diversity statistics for 16-locus microsatellite genotypes and mitochondrial HV2 sequences. Site labels represent two-letter state codes as in Fig. 1 time. Our study provides valuable data for understanding the population-level impacts of mortalities due to wind power for this migratory bat species by assessing whether there are discrete subpopulations that may represent independent management units and may undergo different migratory behavior, whether populations from different ...
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... to be resident) primarily between 2000 and 2006, for the purpose of assessing levels of genetic population structure and estimating N e (Table 1 and Table S1). We received tissue samples for 1-39 bats from any given site. We had sufficient sample size (N > 15) for each of 12 sites with which to carry out site-level population genetic analyses ( Fig. 1 and Table 1). Unlike colonial bats roosting in buildings or trees where bats can be captured in numbers from a single point location during a single sampling session, tree-roosting bats such as eastern red bats are solitary. Sampling these bats therefore must involve the capture of foraging individuals and may encompass individuals ...
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... vs. B1-B3 for 2010). For the current effective population size N 1 , we recovered generally consistent estimates on the order of 10 4 -10 5 (average N 1 ≈ 74,500). Estimates of ancestral effective population size N A were less consistent among runs, but did result in estimates ranging in the same order of magnitude as N 1 (average N A ≈ 194,300; Fig. S1). These analyses yielded differing signals of population growth vs. decline between runs (Table 5), although a majority of runs (8 of 11) support a model of population decline rather than growth. The time of this population size change (t) was also variable among runs, but generally was on the order of 10 3 -10 4 years (average t ≈ ...

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Documented fatalities of bats at wind turbines have raised serious concerns about the future impacts of increased wind power development on populations of migratory bat species. However, for most bat species we have no knowledge of the size of populations and their demographic trends, the degree of structuring into discrete subpopulations, and whet...

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... The available data for these two species is limited to basic occurrence records, reproductive data, minimal genetic libraries, and disjunct regional studies (Cryan 2006, Solick et al. 2020). At the most basic level, there is substantial ambiguity regarding their distribution and speciation (Vonhof 2015;O'Shea & Bogan, 2003;Kunz et al. 2009). This study aimed to fill critical information gaps on the relationship and current distribution between L. borealis and L. frantzii for effective management and conservation going forward. ...
... Since high levels of gene flow was found in Eastern red bats, and little is known of Western red bat connectivity, the effects of wind turbines in one locality can affect red bats nationwide. indicating that monitoring and management should integrate curtailment across the entirety of their range (Korstian 2006, Murtaugh et al. 2019, Vonhof and Russell 2015. ...
... With these two observations, there is sufficient data to hypothesize that L. frantzii occupants in the West comprise multiple subpopulations with unknown connectivity and gene flow. As L. borealis have been hypothesized to be a single panmictic population(Korstian 2006, Sovick et al. 2016, Vonhof and Russell 2015, the variation seen in L. frantzii exemplifies that the two species are not only genetically distinct but largely different behaviorally from one another.Moving forward, we predict that sequencing the mitochondrial control region may be informative about genetic connections among distant roosts and migratory connections (Flemming 2019). In addition genomic approaches to population genetics could give us high quality results using less samples if capture is not as efficient or possible. ...
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Several recent accounts of overlap and historic misidentifications regarding two species of the genus Lasiurus, Western red bat (Lasiurus frantzii) and Eastern red bat (Lasiurus borealis), have cast doubt on our understanding of their distribution, assumed spatial allopatry, and interactions in the United States Southwest. With the use of morphometrics and genetic sequencing, utilizing tissue collected from specimens throughout California and adjoining states, we have reassessed the current distribution, best practices for field identification, and genetic differentiation between both species. Appropriate species classification by region was achieved utilizing mitochondrial DNA, targeting the cytochrome c oxidase subunit I gene, and genetic discrepancies were assessed through lower coverage whole genome sequencing (lcWGS). All samples included morphometrics and pelage records to identify possible congruence in segregating the species phenotypically. We have confirmed L. borealis in four counties in southern California, one county in northern California, and 1 county in southern Arizona, displaying sympatry between both L. frantzii and L. borealis in the west. The lcWGS results verified the high level of divergence and genetic segregation between both species indicating little to no hybridization potential. No conclusive morphometric differentiation could be distinguished through physical metrics, but pelage has proven to have consistent discrepancies by region. The extent of L. borealis in the Western United States seems limited to the southern most areas of each state in the Southwest, but more sampling will be necessary to infer their true extent. The results acquired from this study strengthens our limited understanding of this dynamic group by inferring on their basic biology, their distinctive characteristics, and altogether aid in future conservation and research.
... Historically, eastern red bats have not been of special conservation concern. However, they frequently die at wind power installations, and there is evidence that these mass mortality events are causing range-wide population declines in this species (Vonhof and Russell, 2015;Bombaci et al., 2021;Davy et al., 2021). While most of the protected bat species in North America are closed-space specialists, eastern red bats are edge specialists, with broadband, moderate-frequency echolocation calls and high wing loading, which makes them well suited for flying and capturing insects in semi-open to open spaces (Norberg and Rayner, 1987;Aldridge and Rautenbach, 1987). ...
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... Migratory tree-roosting bats are more likely impacted by wind energy development than cave-hibernating species, however their population sizes are difficult to determine due to small roosts and dispersal across the landscape. The best current estimates from genetic analysis suggest the effective population size (size of the ideal population that would experience the same amount of genetic drift as the observed population) of the Eastern red bat is 100,000s-1,000,000s, the silver-haired bat is 100,000s, and the hoary bat is 1,000s-100,000s (Korstian et al. 2015, Vonhof & Russell 2015, Pylant et al. 2016, Sovic et al. 2016, Ammerman et al. 2019. Bat mortality data from wind energy development comes from land-based wind, however, as bats are also active offshore, inference from onshore can be applied to offshore. ...
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... This contrasts with our hypothesis where we expected to find some evidence of restricted gene flow due to the limited distribution and availability of suitable roosts throughout the landscape and indicates Pilbara leaf-nosed bats have higher population connectivity than previously thought. Other studies on microbats using nuclear markers have reported high levels of gene flow and well connected populations in migratory (Chipps et al., 2020;Korstian et al., 2015;Vonhof and Russell, 2015), tropical island (Pinzari et al., 2020), and widely-occurring Australian tree-dwelling bat species (Fuller, 2013;Prada, 2020). Breeding behaviour, such as swarming during mating can also facilitate gene flow (Burns and Broders, 2015;Kerth et al., 2003), though it is unknown whether this phenomenon occurs in Pilbara leaf-nosed bats. ...
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