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22 March 2013 Isolation and Characterization of Microsatellite Loci in the Invasive Herb Solidago altissima (Asteraceae)
Yuzu Sakata, Shingo Kaneko, Azusa Hayano, Miho Inoue-Murayama, Takayuki Ohgushi, Yuji Isagi
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Tall goldenrod (Solidago altissima L.; Asteraceae) is considered to be among the most invasive of introduced plants in Japan (Shimizu, 2003), China (Huang and Guo, 2004), and Taiwan (Li, 1978). It is a rhizomatous herbaceous perennial native to a variety of successional habitats such as prairies, woodland edges, and old fields throughout eastern North America. Diploid, tetraploid, and hexaploid cytotypes are known to occur at a continental scale and even on very fine spatial scales in some local populations in its native range (Halverson et al., 2008), while only hexaploids have been found in Japan (Sakata, unpublished data). After the species was introduced to Japan in the early 19th century as an ornamental plant, it has continuously expanded its range and has now invaded disturbed areas throughout Japan (Shimizu, 2003). Two closely related species, S. canadensis L. and S. gigantea Aiton, have also become invasive throughout Europe. Solidago altissima is also well studied as a model plant for insect—plant interactions, and effects of the variation among its genotypes on the diversity and composition of foliage-based arthropods have been studied (e.g., Crutsinger et al., 2008). However, these studies used amplified fragment length polymorphism (AFLP) analysis to identify individuals and calculate the genotypic diversity of S. altissima, and no microsatellite markers are available for population genetic studies. There is a great need for molecular studies that address pathways of introduction, genetic variability within and between populations, and the potential for rapid evolutionary changes in tall goldenrod since its introduction. Here we report 16 nuclear microsatellite loci for S. altissima developed using 454 next-generation sequencing, which will facilitate studies on the invasion dynamics and population genetics of the species.

METHODS AND RESULTS

A fresh leaf sample of S. altissima was collected from an individual grown at the greenhouse of the Center for Ecological Research, Kyoto University, Japan (34.97136°N, 135.957892°E). A voucher was deposited at KYO (accession number: 00020479). Genomic DNA was extracted using a DNeasy Plant Mini Kit (QIAGEN, Germantown, Maryland, USA). A DNA library for S. altissima was constructed using the GS Junior Titanium Series kit (Roche, Mannheim, Germany). A 500-ng aliquot of the genomic DNA was nebulized at 0.24 MPa for 1 min and purified using the MinElute PCR Purification Kit (QIAGEN). The purified DNA fragments were end-repaired and A-tailed using the Rapid Library Preparation Kit (Roche) and ligated to the Rapid Library Adapter (Roche) with RL Ligase (Roche). Suitably sized DNA fragments were selected by removing short fragments with AMPure XP beads (Beckmann Coulter, Brea, California, USA). Fragments were then mixed with capture beads and amplified by emulsion polymerase chain reaction (emPCR) from the DNA library with the GS Junior Titanium emPCR Kit (Roche). After emPCR, beads were collected, and beads capturing the DNA library were enriched before annealing with sequencing primers to selectively capture beads with sequenceable amounts of template DNA. Amplified fragments were sequenced using the GS Junior Benchtop system (Roche), obtaining 70,602 DNA sequences.

The sequences were screened for potential microsatellite loci by MSATCOMMANDER (Faircloth, 2008). We screened sequences for ≥8 dinucleotide repeats and ≥6 trinucleotide repeats using the Primer3 software (Rozen and Skaletsky, 2000) embedded in MSATCOMMANDER. A total of 2629 repeats were found, consisting of 2082 dinucleotide and 547 trinucleotide repeats. Primers were successfully designed for a total of 370 repeats, including 156 dinucleotide and 214 trinucleotide repeats. Based on the repeat structure and avoiding sequences containing mononucleotide repeats, 84 primer pairs (23 dinucleotide and 61 trinucleotide loci) were selected for amplification trials in eight individuals from throughout the invasive range of S. altissima. For all the loci, the forward primer was synthesized with a tag sequence (5′-CACGACGTTGTAAAACGAC-3′) (Boutin-Ganache et al., 2001). PCR amplifications were performed according to a modified protocol using the QIAGEN Multiplex PCR Kit (QIAGEN). The PCR reaction mixture had a final volume of 5 µL, which included 16 ng of extracted DNA, 2.5 µL of Multiplex PCR Master Mix, 0.01 µM of forward primer, 0.2 µM of reverse primer, and 0.1 µM of M13 (fluorescently labeled) primer. The amplification profiles included an initial denaturation at 95°C for 15 min, followed by 30 cycles of 30 s at 94°C, 1.5 min at 57°C, and 1 min at 72°C, and a final extension for 30 min at 60°C. PCR product size was measured using the ABI PRISM 3100 Genetic Analyzer (Applied Biosystems, Foster City, California, USA) and Genotyper version 4 (Applied Biosystems). Of these, 15 trinucleotide primers and one dinucleotide primer amplified well and were easy to score unambiguously (Table 1). The 68 primer pairs remaining failed to produce the expected product size or were not consistently amplifiable. The 16 successful primer pairs were amplified in 70 individuals sampled from three populations located in northern, central, and southern Japan (Hokkaido: 43.057372°N, 141.508487°E; Hyogo: 34.41131°N, 135.16072°E; Kagoshima: 31.613611°N, 130.420487°E) with the same protocol used in the amplification test described above. One sample from each population has been vouchered at KYO (accession numbers: 00020488-00020490).

TABLE 1.

Characteristics of 16 microsatellite primers developed in Solidago altissima. All values are based on 70 samples representing Japanese populations located in Hokkaido, Hyogo, and Kagoshima (N = 22-24 for each).

t01_01.gif

TABLE 2.

Results for primer screening of all samples of 16 microsatellite loci from three populations of Solidago altissima.

t02_01.gif

Number of alleles per locus (A), gametic heterozygosity (Ho) (Moody et al., 1993), and expected heterozygosity (He) were calculated by the program GenoDive version 2.0b19 (Meirmans and Van Tienderen, 2004) for each polymorphic locus over each population. Probability of identity (PID) (Waits et al., 2001) was obtained to indicate if these loci are useful for fingerprinting analysis and analyzing clonal structure of S. altissima after calculating the allele frequency of 70 samples by POLYSAT (Clark and Jasieniuk, 2011) using the function “simpleFreq.” For all samples in all populations, the number of alleles per polymorphic locus ranged from five to 25, Ho from 0.31 to 0.99, He from 0.46 to 0.92, and PID from 0.006 to 0.48. The values of A, Ho, He, and PID for each polymorphic locus over each population are given in Table 2.

CONCLUSIONS

We have characterized 16 microsatellite loci for the invasive herb S. altissima. These microsatellite loci will be useful for investigating the genetic structure, contemporary gene flow, fingerprinting, and invasion dynamics of S. altissima.

LITERATURE CITED

1.

I. Boutin-Ganache , M. Raposo , M. Raymond , and C. F. Deschepper . 2001. M13-tailed primers improve the readability and usability of microsatellite analyses performed with two different allele-sizing methods. BioTechniques 31: 24–26. Google Scholar

2.

L. V. Clark , and M. Jasieniuk . 2011. POLYSAT: An R package for polyploid microsatellite analysis. Molecular Ecology Resources 11: 562–566. Google Scholar

3.

G. M. Crutsinger , W. N. Reynolds , A. T. Classen , and N. J. Sanders . 2008. Disparate effects of plant genotypic diversity on foliage and litter arthropod communities. Oecologia 158: 65–75. Google Scholar

4.

B. C. Faircloth 2008. MSATCOMMANDER: Detection of microsatellite repeat arrays and automated, locus-specific primer design. Molecular Ecology Resources 8: 92–94. Google Scholar

5.

K. Halverson , S. B. Heard , J. D. Nason , and J. O. Stireman III . 2008. Origins, distribution, and local co-occurrence of polyploid cytotypes in Solidago altissima (Asteraceae). American Journal of Botany 95: 50–58. Google Scholar

6.

H. Huang , and S. Guo . 2004. Review on ecological studies on three invasive species of European genus Solidago. Guangxi Sciences 11: 69–74. Google Scholar

7.

H. L. Li 1978. Compositae. Flora of Taiwan, vol. 4, 768–965. Epoch Publishing Co, Taipei, Taiwan. Google Scholar

8.

P. G. Meirmans , and P. H. Van Tienderen . 2004. GENOTYPE and GENODIVE: Two programs for the analysis of genetic diversity of asexual organisms. Molecular Ecology Notes 4: 792–794. Google Scholar

9.

M. E. Moody , L. D. Mueller , and D. E. Soltis . 1993. Genetic-variation and random drift in autotetraploid populations. Genetics 134: 649–657. Google Scholar

10.

S. Rozen , and H. Skaletsky . 2000. Primer3 on the WWW for general users and for biologist programmers. Methods in Molecular Biology (Clifton, N.J.) 132: 365–386. Google Scholar

11.

T. Shimizu 2003. Naturalized plants of Japan. Heibonsya, Tokyo, Japan. Google Scholar

12.

L. P. Waits , G. Luikart , and P. Taberlet . 2001. Estimating the probability of identity among genotypes in natural populations: Cautions and guidelines. Molecular Ecology 10: 249–256. Google Scholar

Notes

[1] This work was supported by the Japan Society for the Promotion of Science (JSPS) Core-to-Core Program (No. 20004) from JSPS and the Environment Research and Cooperation Research Program of the Wildlife Research Center, Kyoto University.

Yuzu Sakata, Shingo Kaneko, Azusa Hayano, Miho Inoue-Murayama, Takayuki Ohgushi, and Yuji Isagi "Isolation and Characterization of Microsatellite Loci in the Invasive Herb Solidago altissima (Asteraceae)," Applications in Plant Sciences 1(4), (22 March 2013). https://doi.org/10.3732/apps.1200313
Received: 20 June 2012; Accepted: 1 September 2012; Published: 22 March 2013
KEYWORDS
454 sequencing
Asteraceae
invasion
polyploidy
Solidago altissima.
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