Skip to main content
Applications in Plant Sciences logoLink to Applications in Plant Sciences
. 2015 Apr 7;3(4):apps.1400120. doi: 10.3732/apps.1400120

Characterization of 23 polymorphic SSR markers in Salix humboldtiana (Salicaceae) using next-generation sequencing and cross-amplification from related species1

Jorge A Bozzi 2,6, Sascha Liepelt 3, Sebastian Ohneiser 3, Leonardo A Gallo 2, Paula Marchelli 2,4, Ilona Leyer 3,5, Birgit Ziegenhagen 3, Christina Mengel 3
PMCID: PMC4406835  PMID: 25909042

Abstract

Premise of the study:

We present a set of 23 polymorphic nuclear microsatellite loci, 18 of which are identified for the first time within the riparian species Salix humboldtiana (Salicaceae) using next-generation sequencing.

Methods and Results

To characterize the 23 loci, up to 60 individuals were sampled and genotyped at each locus. The number of alleles ranged from two to eight, with an average of 4.43 alleles per locus. The effective number of alleles ranged from 1.15 to 3.09 per locus, and allelic richness ranged from 2.00 to 7.73 alleles per locus.

Conclusions

The new marker set will be used for future studies of genetic diversity and differentiation as well as for unraveling spatial genetic structures in S. humboldtiana populations in northern Patagonia, Argentina.

Keywords: next-generation sequencing, nuclear microsatellite marker, river margins, Salicaceae, Salix humboldtiana


The diploid Salix humboldtiana Willd. (Salicaceae) is the only native Salix L. species in the southern hemisphere (Becerra et al., 2009). This dioecious species forms dense natural stands on wet sand banks of river margins (Tortorelli, 2009). Its natural distribution range, one of the widest among Argentinean native woody species, reaches from Mexico in the northern hemisphere to Argentina and Chile on the 45th parallel in the southern hemisphere (Tortorelli, 2009). In northern Patagonia, floodplain forests structured by S. humboldtiana have been displaced by mixed forests dominated by Eurasian invasive willows and poplars (Thomas and Leyer, 2014). Together with landscape fragmentation and alterations of the hydrological regime caused by dam construction, these invasion processes represent a serious threat to this species in northern Patagonian riparian ecosystems. In addition, there is genetic evidence of hybridization between S. humboldtiana and invasive willows (Bozzi et al., unpublished). Programs for conserving its genetic resources and genetic diversity should be established. Therefore, knowledge is needed about nuclear genetic diversity. To be able to perform these analyses, we developed markers for ongoing population genetic research in S. humboldtiana. Additionally, we tested cross-amplification in S. humboldtiana of markers previously developed for related species.

METHODS AND RESULTS

For primer testing and diversity assessment, a total of 60 S. humboldtiana individuals were sampled at the Río Negro in Argentina. DNA was extracted from dried leaves following the protocol by Dumolin et al. (1995). A novel set of microsatellite markers specific for S. humboldtiana was developed using a next-generation sequencing approach (Table 1). 454 sequencing was performed by Ecogenics (Zurich-Schlieren, Switzerland) as follows: DNA was enriched for two repeat motifs (CT and GT) representing all enrichable dinucleotide motifs, and sequenced on a GS FLX (Roche Applied Science, Indianapolis, Indiana, USA) after library construction. A FASTA file was provided with a total of 14,714 reads covering 2.23 Mb and exhibiting an average read length of 152 bases and a mode of 101 bases (sequence data available upon request). We used the software QDD (Meglécz et al., 2010) to assemble the reads and screen for di-, tri-, tetra-, penta-, and hexanucleotide repeats. The screening was performed using default settings except for the minimum length of PCR product, which was set to 80 bp. The software Primer3 (Rozen and Skaletsky, 1999), included in QDD, was used to design primer pairs for PCR for 67 sequences containing microsatellite motifs with the specified characteristics. We discarded all loci (eight sequences) showing compound or interrupted simple sequence repeats (SSRs). Moreover, from the 59 sequences that showed a perfect microsatellite motif, 17 loci had to be removed because they showed undesirable properties such as poor sequence quality in the flanking region or SSR stretches too close to the end of the read. Primer pairs for the remaining 42 loci were ordered from Metabion (Martinsried, Germany). Additionally, 24 extra primer pairs suggested by Ecogenics, and 24 primer pairs previously developed for related species were tested (Salix alba L. [King et al., 2010], S. lanata L. [Stamati et al., 2003], Populus trichocarpa Torr. & A. Gray [Tuskan et al., 2004; International Populus Genome Consortium: http://www.ornl.gov/sci/ipgc/ssr_resource.htm], S. burjatica Nasarow [Hanley et al., 2002; Barker et al., 2003], S. arbutifolia Pall. [Hoshikawa et al., 2009], P. nigra L. [Van der Schoot et al., 2000; Smulders et al., 2001], and S. hukaoana Kimura [Kikuchi et al., 2005]). Fluorescent labeling using M13 primer tails was performed according to Schuelke (2000) to test this high number of loci in a cost-efficient way. We used a subset of eight individuals to prescreen the quality of the amplified SSRs on a MegaBACE 1000 automated capillary sequencer (GE Healthcare, Freiburg, Germany). Scorable polymorphic bands were revealed by 23 SSR loci (Table 2), while no amplification, pronounced stutter bands, multibanding patterns, or monomorphic bands were shown by the remaining 67 loci. To further characterize the 23 selected loci, the number of analyzed samples was increased to at least 22 and up to 60 individuals. Only 14 loci were screened using 60 individuals belonging to two populations (Appendix 1), while the remaining loci were evaluated with a panel of individuals sampled at different locations along the river. Fluorescence-labeled primers were ordered for those loci with a high level of polymorphism and good scorability. PCRs were performed in a 16.6-μL mix containing 1.2 ng/μL of template DNA, 1× PCR reaction buffer (Molegene, Butzbach, Germany), 0.3 mM of each dNTP (Bioline, Luckenwalde, Germany), 0.04 U/μL of Taq polymerase (Molegene), 0.2 μM of each primer (Metabion), 0.16 mg/mL of bovine serum albumin (BSA; Thermo Scientific, St. Leon-Rot, Germany), and 2.4–3.0 mM of MgCl2 (Molegene), depending on the locus to be amplified (Table 3). PCR amplification was conducted using a T1 Thermocycler (Biometra, Göttingen, Germany) performed with 5 min of initial denaturation at 94°C, followed by 30–40 cycles of 30–45 s of denaturation at 94°C, 45 s of annealing at 53–60°C, 30–45 s of elongation at 72°C, and 10 min of final elongation at 72°C. For some primer pairs, a touchdown PCR was conducted. The cycling process of the touchdown PCR was performed with 30–45 s of denaturation at 94°C, 45 s of annealing with temperatures decreasing 1°C per cycle from 65–60°C to 56–51°C during the first 10 cycles and temperatures of 57–60°C for the last 20–25 cycles, and 30–45 s of elongation at 72°C (Table 3). Primer pairs are reported in Table 1.

Table 1.

Characteristics of 18 nuclear microsatellite loci developed in Salix humboldtiana.

Locus Primer sequences (5′–3′) Repeat motif Allele size range (bp) GenBank accession no.
Shum_002 F: ACTTGCAGGGGTGTCTACTG (AC)13 100–106 KP208969
R: AGGTCAAAACATTGACATCCAAATTC
Shum_006 F: CAACACAACACAACAACGCA (AACAC)8 102–117 KP208970
R: GGAGAAAGATCTCCGCTTTG
Shum_029 F: TAAGCTACCCCTGACAACCC (AC)13 107–109a KP208971
R: AGCCCCATGAATAATCCCCG
Shum_032 F: ACCAAGCTGGCAATATGGAG (AGC)6 101–128 KP208972
R: CCGTTTGGAACTTTGTGATG
Shum_033 F: AATGAGCAGTGCCTTTTGAC (CA)19 105–109a KP208973
R: GAACATGTGGGTCGTTCTCC
Shum_047 F: TGCAAATCCATAATGACTTCTTTC (AC)19 121–133 KP208974
R: GCCTAGGCCACTTTGTGTTC
Shum_049 F: TATCCATCTTTCGAGCTGGC (AC)13 237–241a KP208975
R: TCTCGCTCTATCTGCCATCA
Shum_060 F: TGACACGCATCCCTTCTGTG (AC)20 110–130 KP208976
R: ACAGTTCTGAATGCCAGTCTC
Shum_061 F: TATTTTGATTCGAGCCCCCG (GT)19 108–116 KP208977
R: TTTCGTCCACTCTGGCTTCC
Shum_062 F: TTTAAGAACGATGGTGGGGG (AC)17 162–168a KP208978
R: TCCTTGTACCCGAGTTCTGC
Shum_064 F: ATGTCCAAGAGTGCGCTATG (GT)16 99–103 KP208979
R: GACTAGTTGTGCAGTACACGC
Shum_066 F: ATTTGATCGCGGAGGTCACG (AC)16 115–129 KP208980
R: ACCTTATGTTTCCTTTTAATGTTGAG
Shum_067 F: TCAAATGCGCCGGGATAAATAG (GT)16 100–112a KP208981
R: AGCTCATACCAACCACATCTAC
Shum_070 F: ATCGGATGGATCGGGCATAG (AC)15 161–167 KP208982
R: GAGGGGAGTACACTCTAAAACC
Shum_071 F: GTAACAGACTTGGCAACCCG (CA)14 244–248 KP208983
R: TTGGCGGCTTCCATTACATC
Shum_074 F: TTCCAGCCTTAGATTGCTTGC (AC)13 82–86 KP208984
R: GTCAACTCAGCTGCCATTCG
Shum_076 F: TATCTGATCCACCCCATGCC (CA)13 141–153 KP208985
R: TTACAACTCTGCAATAGTAAGATCC
Shum_077 F: AGTAGTTTTCGCATACGCTG (TG)13(AC)13 180–192 KP208986
R: ATGTCACTGGTAGAGGACGC
a

Fragment size calculated by discounting 18 bp belonging to the M13 fragment.

Table 2.

Characteristics of 23 nuclear microsatellite loci developed in this and other studies for Salix humboldtiana.

RNo03b RNo13b
Locusa N A AR Ae Ho Hec Ho Hec
Shum_002 60 4 3.98 2.42 0.517 0.563ns 0.677 0.598ns
Shum_006 36 3 2.61 1.73
Shum_029 31 2 2.00 1.29
Shum_032 60 4 3.85 1.40 0.103 0.267** 0.355 0.301ns
Shum_033 53 3 3.00 1.92 0.680 0.473ns 0.786 0.477***
Shum_047 60 7 6.83 2.33 0.414 0.555ns 0.516 0.571ns
Shum_049 32 3 2.69 1.21
Shum_060 53 6 5.96 2.10 0.542 0.531ns 0.586 0.505ns
Shum_061 56 5 5.00 3.09 0.654 0.637ns 0.667 0.701ns
Shum_062 31 4 3.42 2.13
Shum_064 53 3 2.98 2.00 0.458 0.510ns 0.517 0.490ns
Shum_066 60 8 7.73 2.46 0.448 0.488ns 0.613 0.668ns
Shum_067 32 4 3.37 1.29
Shum_070 59 4 3.76 1.17 0.071 0.070ns 0.194 0.203*
Shum_071 59 3 2.88 1.44 0.321 0.275ns 0.226 0.331ns
Shum_074 59 3 3.00 1.15 0.036 0.035ns 0.226 0.207ns
Shum_076 58 5 4.78 1.19 0.071 0.135** 0.200 0.186ns
Shum_077 52 5 5.00 1.30 0.083 0.081ns 0.393 0.340ns
Sa54A 60 7 6.86 2.74 0.414 0.508ns 0.710 0.721ns
gSIMCT24 43 7 5.24 1.49
ORPM446 22 3 3.00 1.50
SB196 29 3 3.00 1.64
WPMS18 32 6 5.71 1.73

Note: A = number of alleles; Ae = effective number of alleles; AR = allelic richness standardized by rarefaction; He = expected heterozygosity; Ho = observed heterozygosity; N = number of individuals analyzed.

a

Previously developed loci: Sa54A (King et al., 2010); gSIMCT24 (Stamati et al., 2003); ORPM446 (Tuskan et al., 2004); SB196 (Barker et al., 2003); WPMS18 (Smulders et al., 2001).

b

Values of He and Ho are not shown for loci evaluated with a panel of individuals that were not part of populations RNo03 or RNo13.

c

Significant deviations from Hardy–Weinberg equilibrium: *P < 0.05; **P < 0.01; ***P < 0.001; ns = not significant.

Locus showing null allele at one of the analyzed populations.

Table 3.

Summary list of PCR cocktail MgCl2 content and cycle profiles for 23 polymorphic nuclear microsatellite markers amplified in Salix humboldtiana.

Cycle profilec
Locusa MgCl2 (mM)b Cycle profilec No. of cycles
Denaturation (s) Ta (°C) Elongation (s)
Shum_002 2.6 35 60 35 30
Shum_032 3.0 40 55 40 35
Shum_033 3.0 40 54 40 35
Shum_047 3.0 30 55 30 35
Shum_060 3.0 30 60 30 30
Shum_061 3.0 30 58 30 40
Shum_064 3.0 30 TD (60/51) 57 30 10–25
Shum_066 3.0 35 TD (63/54) 59 35 10–25
Shum_070 3.0 40 TD (61/52) 58 40 10–20
Shum_071 2.7 40 56 40 34
Shum_074 2.6 30 57 30 30
Shum_076 2.7 45 TD (65/56) 60 45 10–23
Shum_077 3.0 40 54 40 40
Shum_006 2.6 30 53 30 30
Shum_029 3.0 45 57 45 35
Shum_049 3.0 45 57 45 35
Shum_062 3.0 45 55 45 35
Shum_067 3.0 45 TD (60/51) 57 45 10–25
Sa54A 2.6 40 59 40 35
gSIMCT24 2.4 45 54.5 45 33
ORPM446 3.0 45 55 45 30
SB196 3.0 45 54 45 30
WPMS18 3.0 45 59 45 35

Note: Ta = annealing temperature.

a

Previously developed loci: Sa54A (King et al., 2010); gSIMCT24 (Stamati et al., 2003); ORPM446 (Tuskan et al., 2004); SB196 (Barker et al., 2003); WPMS18 (Smulders et al., 2001).

b

MgCl2 content in the PCR cocktails.

c

Denaturing temperature 94°C; annealing cycle run for 45 s; TD = touchdown PCR, with the range of annealing temperatures for the first 10 cycles in parentheses; elongation temperature 72°C.

A MegaBace 1000 automated capillary sequencer (GE Healthcare) was used to separate the SSR amplicons by capillary electrophoresis. For allele sizing, the internal size standard MegaBACE ET400-R (GE Healthcare) and MegaBACE Genetic Profiler software (version 1.2; GE Healthcare) were used.

Genetic diversity parameters (Table 2) and deviations from Hardy–Weinberg equilibrium (HWE) were estimated using GenAlEx version 6.5 (Peakall and Smouse, 2012). The number of alleles ranged from two to eight with an average of 4.43 alleles per locus, while the effective number of alleles ranged from 1.15 to 3.09 per locus. Allelic richness standardized by rarefaction was estimated according to El Mousadik and Petit (1996), and values ranged from 2.0 to 7.73 alleles per locus. The observed and expected heterozygosities ranged from 0.036 to 0.786 and 0.035 to 0.721, respectively. Significant deviation from expected heterozygote frequencies was observed for Shum_070 (P < 0.05); Shum_032 and Shum_076 (P < 0.01); and Shum_033 (P < 0.001). The software MICRO-CHECKER version 2.2.3 (van Oosterhout et al., 2004) was used to detect null alleles, and evidence for null alleles was detected at only one locus (Shum_032) in one population. Deviation from HWE can be explained by the presence of null alleles in the case of Shum_032. Inbreeding due to small effective population size can explain deviations from HWE in the case of Shum_033, Shum_070, and Shum_076. Fisher’s exact test analysis to detect linkage disequilibrium was performed using GENEPOP version 4.3 (Rousset, 2008). Linkage disequilibrium (P < 0.05) was detected between two loci: Shum_002 and Shum_070 (Table 2).

CONCLUSIONS

In the near future, the described microsatellite markers will be used to analyze the genetic structure and diversity of S. humboldtiana along river stretches in northern Patagonia, Argentina, and to unravel dispersal processes as well as effects of landscape fragmentation and biological invasions. To our knowledge, no SSR markers had been previously developed for S. humboldtiana. The new marker set can be used for future studies of genetic diversity and differentiation as well as for estimating dispersal distances and determining spatial genetic structures. Beyond population genetic applications, these markers may also be useful for clone identification, genome mapping, and breeding purposes. Furthermore, they may be useful in testing for cross-amplification in related species and developing PCR multiplexes for fast and economic genotyping.

Appendix 1.

Voucher and location information for the Salix humboldtiana populations used in this study. The vouchers are deposited in Herbarium Marburgense, University of Marburg, Marburg, Germany.

Population Locality Geographic coordinates N Voucher no. Herbarium ID Collector
RNo03 Allen, Río Negro, Argentina 39°2′43.50″S, 67°47′44.34″W 29 RNo03-26 MB-001506 Bozzi, J.
RNo13 Beltrán, Río Negro, Argentina 39°16′13.96″S, 65°49′26.86″W 31 RNo13-06 MB-001538 Bozzi, J.

Note: N = number of individuals sampled.

LITERATURE CITED

  1. Barker J. H. A., Pahlich A., Trybush S., Edwards K. J., Karp A. 2003. Microsatellite markers for diverse Salix species. Molecular Ecology Notes 3: 4–6. [Google Scholar]
  2. Becerra A. G., Nouhra E. R., Silva M. P., McKay D. 2009. Ectomycorrhizae, arbuscular mycorrhizae, and dark-septate fungi on Salix humboldtiana in two riparian populations from central Argentina. Mycoscience 50: 343–352. [Google Scholar]
  3. Dumolin S., Demesure B., Petit R. J. 1995. Inheritance of chloroplast and mitochondrial genomes in pedunculate oak investigated with an efficient PCR method. Theoretical and Applied Genetics 91: 1253–1256. [DOI] [PubMed] [Google Scholar]
  4. El Mousadik A., Petit R. J. 1996. High level of genetic differentiation for allelic richness among populations of the argan tree [Argania spinosa (L.) Skeels] endemic to Morocco. Theoretical and Applied Genetics 92: 832–839. [DOI] [PubMed] [Google Scholar]
  5. Hanley S., Barker A., Van Ooijen W., Aldam C., Harris L., Ahman I., Larsson S., Karp A. 2002. A genetic linkage map of willow (Salix viminalis) based on AFLP and microsatellite markers. Theoretical and Applied Genetics 105: 1087–1096. [DOI] [PubMed] [Google Scholar]
  6. Hoshikawa T., Kikuchi S., Nagamitsu T., Tomaru N. 2009. Eighteen microsatellite loci in Salix arbutifolia (Salicaceae) and cross-species amplification in Salix and Populus species. Molecular Ecology Resources 9: 1202–1205. [DOI] [PubMed] [Google Scholar]
  7. Kikuchi S., Suzuki W., Ban N., Kanazashi A., Yoshimaru H. 2005. Characterization of eight polymorphic microsatellites in endangered willow Salix hukaoana. Molecular Ecology Notes 5: 869–870. [Google Scholar]
  8. King R. A., Harris S. L., Karp A., Barker J. H. A. 2010. Characterisation and inheritance of nuclear microsatellite loci for use in population studies of the allotetraploid Salix albaSalix fragilis complex. Tree Genetics & Genomes 6: 247–258. [Google Scholar]
  9. Meglécz E., Costedoat C., Dubut V., Gilles A., Malausa T., Pech N., Martin J.-F. 2010. QDD: A user-friendly program to select microsatellite markers and design primers from large sequencing projects. Bioinformatics 26: 403–404. [DOI] [PubMed] [Google Scholar]
  10. Peakall R., Smouse P. E. 2012. GenAlEx 6.5: Genetic analysis in Excel. Population genetic software for teaching and research—An update. Bioinformatics 28: 2537–2539. [DOI] [PMC free article] [PubMed] [Google Scholar]
  11. Rousset F. 2008. GENEPOP’007: A complete re-implementation of the GENEPOP software for Windows and Linux. Molecular Ecology Resources 8: 103–106. [DOI] [PubMed] [Google Scholar]
  12. Rozen S., Skaletsky H. 1999. Primer3 on the WWW for general users and for biologist programmers. In S. Misener and S. A. Krawetz [eds.], Methods in molecular biology, vol. 132: Bioinformatics methods and protocols, 365–386. Humana Press, Totowa, New Jersey, USA. [DOI] [PubMed] [Google Scholar]
  13. Schuelke M. 2000. An economic method for the fluorescent labeling of PCR fragments. Nature Biotechnology 18: 233–234. [DOI] [PubMed] [Google Scholar]
  14. Smulders M. J. M., Van Der Schoot J., Arens P., Vosman B. 2001. Trinucleotide repeat microsatellite markers for black poplar (Populus nigra L.). Molecular Ecology Notes 1: 188–190. [Google Scholar]
  15. Stamati K., Blackie S., Brown J. W. S., Russell J. 2003. A set of polymorphic SSR loci for subarctic willow (Salix lanata, S. lapponum and S. herbacea). Molecular Ecology Notes 3: 280–282. [Google Scholar]
  16. Thomas L. K., Leyer I. 2014. Age structure, growth performance and composition of native and invasive Salicaceae in Patagonia. Plant Ecology 215: 1047–1056. [Google Scholar]
  17. Tortorelli L. A. 2009. Maderas y bosques Argentinos, 2nd ed. Orientación Gráfica Editora, Buenos Aires, Argentina. [Google Scholar]
  18. Tuskan G. A., Gunter L. E., Yang Z. K., Yin T., Sewell M. M., DiFazio S. P. 2004. Characterization of microsatellites revealed by genomic sequencing of Populus trichocarpa. Canadian Journal of Forest Research 34: 85–93. [Google Scholar]
  19. Van der Schoot J., Pospíšková M., Vosman B., Smulders M. J. M. 2000. Development and characterization of microsatellite markers in black poplar (Populus nigra L.). Theoretical and Applied Genetics 101: 317–322. [Google Scholar]
  20. van Oosterhout C., Hutchison W. F., Shipley P., Wills D. P. M. 2004. MICRO-CHECKER: Software for identifying and correcting genotyping errors in microsatellite data. Molecular Ecology Notes 4: 535–538. [Google Scholar]

Articles from Applications in Plant Sciences are provided here courtesy of Wiley

RESOURCES