Using nine DNA markers, we examined the distinctions between H. mantegazzianum specimens collected in the Western Caucasus and giant Heracleum specimens gathered from their initial introduction sites located in Northern Russia. Among these markers, seven were chloroplast DNA fragments, namely, rbcL, matK, psbA-trnH, rps16 intron, trnQ-rps16, rps16-trnK, and rpl32-trnL, and two were from nuclear DNA, namely, ITS and ETS.
The markers rbcL and matK DNA exhibited a minimal level of polymorphism in the studied Heracleum samples, rendering them unsuitable for distinguishing not only species within the giant hogweed complex but also some other Heracleum species.
The markers psbA-trnH, rps16 intron, trnQ-rps16, rps16-K, and rpl32-trnL showed varying degrees of polymorphism, but their variability was insufficient for discriminating between H. mantegazzianum specimens collected within the natural range and giant hogweed complex specimens collected in the invasive part of the range.
Our results are in good agreement with previously obtained data on the use of chloroplast DNA fragments for reconstructing the phylogeny and identifying species of the Apiaceae family. The markers rbcL and matK are impractical for distinguishing between species in the Apiaceae family. However, markers such as psbA-trnH, rps16 intron, trnQ-rps16, rps16-K, and rpl32-trnL exhibit varying levels of intraspecific and interspecific variability for different species in this family (Logacheva et al. 2008; Liu et al. 2014).
The nuclear markers ITS and ETS demonstrated a significantly greater ability to differentiate between species of the Apiaceae family. However, the evolution of these sequences does not always correspond well with the evolution of morphological traits of the species (Logacheva et al. 2010; Yu et al. 2011; Liu et al. 2014). Our results indicate that the use of these markers, either individually or in combination, enables the reliable separation of samples of giant invasive hogweed collected from the sites of primary introduction in northern Russia and within the boundaries of the natural range of H. mantegazzianum from other species in this genus. To clarify, both H. mantegazzianum and invasive hogweeds collected within the invasive range of Northern European Russia belong to the same species. All plant samples from the ‘giant Heracleum complex’ collected by us in Northern European Russia a priori identified by us as H. mantegazzianum, H.sosnowskyi, and H. sosnowskyi × H. mantegazzianum should be identified as H. mantegazzianum.
As mentioned in the introduction, the populations of giant invasive hogweed from the Murmansk region and the Komi Republic were used as the foundation for planting these plants in most of their current invasive habitats. According to our research findings, we can confidently state that the invasive range of H. mantegazzianum includes not only Western Europe but nearly the entire European continent.
These results lead us to two possible conclusions. First, H. mantegazzianum hogweed, but not H. sosnowskyi, may have been introduced to the North of Russia (Murmansk region and the Komi Republic) in the mid-20th century. Alternatively, H. sosnowskyi hogweed could be considered a synonym for H. mantegazzianum. We currently do not have adequate data to support the preceding statement. For this reason, it is necessary to gather samples for herbarization and sequencing from the areas where type specimens of H. sosnowskyi were previously collected; this includes the vicinity of Lelovani village, located in the Adigeni Municipality of the Samtskhe-Javakheti region in Georgia. We also need to collect samples from other locations detailed in Ida Mandenova's monograph (1950) where H. sosnowskyi samples were obtained.
Our results appear to contradict a comprehensive study on the genetic diversity of the giant hogweed complex by Jahodová et al. (Jahodová et al. 2007b). In their study, AFLP-markers were effectively used to determine genetic distances between samples of H. sosnowskyi, H. mantegazzianum, and H. persicum collected from both the invasive and endemic ranges. However, our results demonstrate that although specimens identified as H. sosnowskyi and H. mantegazzianum typically form distinct clusters on the AFLP-derived dendrogram, they actually belong to the same higher-level clade. Within this clade, specimens of H. sosnowskyi and H. mantegazzianum are separated with a bootstrap support of less than 50%. It is also worth noting that the AFLP method allows for the acquisition of a larger number of loci for analysis and, typically, enables the identification of a greater number of homogeneous groups within the studied plant species compared to the use of ISSR and SSR (microsatellite) markers (Nybom 2004).
Population genetic studies of H. mantegazzianum using SSR markers in the UK (Walker et al. 2003) and Finland (Niinikoski and Korpelainen 2015) revealed the presence of distinct groups within this species. In Great Britain, these differences were associated with the boundaries between river catchments. The genetic variances between the two clusters of the eight populations of H. mantegazzianum studied in Finland were attributed to their independent introduction to that country's territory. At the same time, microsatellite markers did not reveal any differences between H. persicum Desf. ex Fisch. and H. rechingeri Manden. (Daemi-Saeidabad et al. 2020). This indicates that distinguishing species within the Pubescentia section of the Heracleum genus solely based on morphological characteristics is controversial.
If samples of H. mantegazzianum plants and giant invasive Heracleum plants collected in the areas of the primary introduction of giant Heracleum species in northern European Russia show inconsistent differences in morphological characters, similar ecological traits and do not differ in DNA markers, it would be appropriate to recognize them simply as a single polymorphic species. It should be acknowledged that there have been no studies on crossbreeding H. sosnowskyi and H. mantegazzianum, as it is impossible to obtain pure lines of both species for such an experiment. Perhaps in the mid-20th century, populations of H. sosnowskyi and H. mantegazzianum from various regions of the Greater Caucasus could still be easily distinguished. However, with the initiation of intensive introduction efforts, the gene pools of both species have intermingled, resulting in the inability to identify H. sosnowskyi in its pure form within the invasive range. To verify the validity of isolating H. sosnowskyi as a distinct species, it is essential to compare the DNA markers of H. mantegazzianum with those of plant material collected from the locus classicus of H. sosnowskyi.
The data obtained from the study revealed that the name H. sosnowskyi is being used in the eastern part of the extensive invasive range of giant hogweed, only in accordance with established tradition. The correct name for most giant invasive Heracleum species in European Russia is H. mantegazzianum.