Next-generation sequencing (NGS) and genomics continue to transform how biologists address fundamental questions in ecology and evolution. The quantity of data that can be generated quickly and cheaply enable researchers to interrogate genomes for hundreds or thousands of loci that can be used for evolutionary inference. This phenomenon had led to an important paradigm shift in how phylogenetic, phylogeographic, and population genomic studies are designed.Historically, mitochondrial DNA (mtDNA) was the primary molecular marker used to estimate evolutionary history and demographic parameters in animals (Avise, 2000;Avise et al., 1987), whereas chloroplast markers were used extensively in plant phylogenetics and phylogeography (Bonatelli et al., 2013;Hickerson et al., 2010;Soltis et al., 1997). Subsequently, microsatellites became a popular multilocus, fragment-based method used to investigate population structure in the nuclear genome. More recently, methods and markers such as RADseq and its derivatives (Baird et al., 2008;Elshire et al., 2011;Peterson et al., 2012), ultraconserved elements (UCEs; Faircloth et al., 2012), anchored hybrid enrichment (AHEs;Lemmon et al., 2012), transcriptomes, and whole genomes have emerged to take full advantage of the power of NGS technologies. The potential resolution provided by thousands of loci is impressive, but not without challenges. Issues with assembly, paralogy, variant calling, phasing, and sequencing errors can all impact subsequent evolutionary inference. Another major issue that can impact these genomic