The domestication of maize took place approximately 9,000 years ago in the Balsas district valley of Mexico, and its first introduction to Europe was in 1493 through the Caribbean by Columbus (Ranere et al., 2009). The cultivation of maize in northern European regions was first reported in Germany in 1539, followed by a rapid expansion that led to immense diversification and adaptation to long days and low temperatures (Tenaillon & Charcosset, 2011). There are also claims of secondary introductions to different northern parts of Europe from North America (Finan, 1948; Tenaillon & Charcosset, 2011). Currently, maize landrace populations are grown over a wide range of latitudes from 25°N to 53°N and at elevations up to 3000 m (X. Wang et al., 2023; Navarro et al., 2017).
Previous reports have characterized European maize landrace populations (EMLPs) within and across countries utilizing morphological differences, such as the number of days to flowering (Gouesnard et al., 1997; Rebourg et al., 2001; Gauthier et al., 2002). EMLPs collected from northeastern Europe for instance were noted for earlier flowering compared to those from southern Europe (Rebourg et al., 2001, P. Gauthier et al., 2002). Despite this, morphological characterizations became inconsistent due to environmental interactions (Rebourg et al., 2001). The extensive adoption of molecular markers, such as isozyme, restriction fragment length polymorphisms (RFLP), and single sequence repeats (SSRs) (Revilla et al., 1998; Dubreuil et al., 1996; Rebourg et al., 1999, Reif et al., 2006), and more recently, single nucleotide polymorphisms (SNPs) from SNP arrays (Ganal et al., 2011; Unterseer et al., 2014; Mayer et al., 2022), largely mitigated this issue. However, discovering large and novel polymorphisms, especially through genotyping-by-sequencing (GBS), should provide a broad genetic base and prevent misinterpretation of diversity studies through ascertainment bias (Inghelandt et al., 2011; Frascaroli et al., 2012). Studies have also revealed the effect of geographic origin on the genetic diversity of maize populations concerning altitude (Tenaillon & Charcosset, 2011; Navarro et al., 2017), longitude, and latitude variations (Gauthier et al., 2002; Revilla et al., 2002; Wang et al., 2017; Diaw et al., 2021).
This diversity can be harnessed to improve the fitness of elite materials in response to changing climates (Navarro et al., 2017; Kawecki & Ebert, 2004), because not all geographic and genetic diversity was captured in selecting the few parental landraces used to develop the elite lines available in Europe today (Strigens et al., 2019), leading to loss of some favorable alleles from the gene pool and limiting their potential for adaptation to extreme climatic conditions (Mayer et al., 2020). Moreover, as the climate changes, new and currently neutral or negative alleles may become desirable for local adaptation, altering the value of populations previously considered less important (Mayer et al., 2020). Local adaptation is assumed when a local population exhibits higher fitness trait values than non-local populations (Janzen et al., 2022). This phenomenon in maize landraces is complex, and the understanding of it is not fully established (Millet et al., 2016; Janzen et al., 2022). Studies have explored methods including multi-environment trials (Navarro et al., 2017), reciprocal transplantation (Nuismer & Gandon, 2008; Gibson et al., 2016; Janzen et al., 2022), and common garden experiments (Clazsen et al., 1940; Fraser et al., 2011; Savolainen et al., 2013) to observe phenotypic variation and functional variants for maize adaptation. While these experimental methods have been useful, they are laborious, costly, and time-consuming.
In this study, we carried out extensive genetic screening of EMLPs to understand their population structure and investigated patterns of genetic diversity across geographic regions. We further identified genomic loci under selection for adaptation to local environments, leveraging each population’s geographical information.