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. 2013 Apr 12;1(5):apps.1200427. doi: 10.3732/apps.1200427

Development and multiplexed amplification of SSR markers for Thuja occidentalis (Cupressaceae) using shotgun pyrosequencing1

Huaitong Xu 2,3,4, Francine Tremblay 2, Yves Bergeron 2
PMCID: PMC4105039  PMID: 25202546

Abstract

Premise of the study: Sixteen novel, polymorphic, multiplexed microsatellite loci were developed for eastern white cedar (Thuja occidentalis) using simple sequence repeat (SSR)–enriched shotgun pyrosequencing.

Methods and Results: Sixteen loci were tested on a panel of 24 individuals from different populations. The number of observed alleles ranged from four to 22. Four sets of multiplex PCR for the 16 loci were then carried out on 60 individuals of two populations from islands of FERLD Duparquet Forest, Canada. Mean number of alleles, observed heterozygosity, and expected heterozygosity were respectively 5.75, 0.594, and 0.574 for Island 58, and 5.50, 0.704, and 0.624 for Island 134.

Conclusions: Four sets of multiplex microsatellite loci can be used for future genetic studies, which includes investigating genetic diversity and structure, and fragmentation and regeneration studies.

Keywords: 454 GS-FLX Titanium, microsatellite marker, next-generation sequencing, population genetics, shotgun pyrosequencing, Thuja occidentalis


Eastern white cedar (Thuja occidentalis L.) is a native, wind-pollinated conifer with a broad distribution across North America (Fowells, 1965). The species’ range extends from the Gulf of St. Lawrence in the east to southeastern Manitoba in the west, and from James Bay in the north to Tennessee and North Carolina in the south (Fowells, 1965). A member of the Cupressaceae, it is also commonly called eastern arborvitae, American arborvitae, northern white cedar, Atlantic red cedar, and swamp cedar in English (USDA NRCS, 2013), and thuya occidental, cèdre, balai, cèdre blanc, thuier cèdre, and arborvitae in French (Brouillet et al., 2010). Eastern white cedar (EWC) is listed as endangered in Indiana, Massachusetts, and New Jersey, as a threatened species in Connecticut, Illinois, Kentucky, and Maryland, and of special concern in Tennessee (USDA NRCS, 2013). Genetic analyses previously conducted on EWC have been mainly based on allozyme markers (Hofmeyer et al., 2007), while highly polymorphic markers such as microsatellites have not been developed for EWC. We report on the development and characterization of microsatellite markers for EWC using shotgun pyrosequencing on a simple sequence repeat (SSR)–enriched library (Malausa et al., 2011).

METHODS AND RESULTS

Foliage of EWC individuals from 14 sites across northern Quebec (Appendix 1) was collected and maintained at −20°C before genetic analysis. Genomic DNA was extracted using the DNeasy Plant Mini Kit (QIAGEN, Hilden, Germany). DNA extracts of 14 individuals were combined and sent on dry ice to Genoscreen (Lille, France) for microsatellite-enriched GS-FLX library construction following the methodology developed by Malausa et al. (2011). Briefly, main steps included: (1) digestion of genomic DNA with RsaI (Fermentas International Inc., Burlington, Ontario, Canada); (2) enrichment of microsatellite sequences in fragmented DNA with eight types of probes (TG, TC, AAC, AAG, AGG, ACG, ACAT, ACTC), which was accomplished by using Dynabeads (Invitrogen, Carlsbad, California, USA); and (3) PCR amplification of enriched DNA with primers specific to the adapter sequences (Malausa et al., 2011). In total, 11,393 raw sequences with an average read length of 400 bp were obtained, with 2175 sequences containing microsatellite motifs. One hundred seventeen of the sequences successfully had primers designed for them using QDD software (Meglécz et al., 2010) using default parameters except optimal primer length of 22 bp (range 18–27 bp) and 50% GC content (range 40–60%).

To minimize screening costs, we initially selected 48 of 117 pairs following criteria detailed in Lepais and Bacles (2011). In brief, we restricted our selection to loci with hexa-, tetra-, and dinucleotide motif types. Dinucleotide motif was limited to AC, CA, TG, GT, AG, GA, CT, and TC types, because AT and TA types are notoriously hard to amplify (Temnykh et al., 2001). Each of the selected 48 loci was initially tested for amplification with unlabeled primers (Invitrogen) on a screening panel that included seven EWC trees collected across northern Quebec (one tree per site) (Appendix 1) and a negative control. Amplifications were carried out in a total volume of 10 μL using four 96-well Mastercycler pro S PCR systems (Eppendorf Gmbh, Wesselling-Berzdorf, Germany). Each reaction mixture contained 1 μL of DNA extract, 5 μL of 2× QIAGEN Multiplex PCR Master Mix (QIAGEN), and a final concentration of 0.2 μM for each forward and reverse primer. The PCR program consisted of an initial heat-activation step at 95°C for 15 min, 36 cycles of three-step cycling (denaturation at 94°C for 30 s, annealing at 54°C for 90 s, extension at 72°C for 60 s), and a final extension at 60°C for 30 min. A total of 2.5 μL of PCR products were visualized on 3% agarose gel (Promega Corporation, Madison, Wisconsin, USA), with electrophoretic migration performed at 100 V for 20 min on the Bio-Rad Imaging System (Bio-Rad, Montreal, Canada).

The initial test on 48 loci using agarose gel showed that 38 had amplified products, and four of 38 had three or more products in one PCR reaction (nonspecific). Among the remaining 34 loci, 16 had one or two amplification products, variable in size. Thus, we used all of them to verify polymorphisms and further design multiplex PCR. Each was tested with fluorescent dye–labeled primers (Applied Biosystems, Carlsbad, California, USA) on a panel that included 24 EWC individuals collected from 24 sites across northern Quebec (one individual per site) (Appendix 1) plus one negative control. PCR cycles were the same as those mentioned previously, except for increased annealing temperatures to achieve specific amplifications (Table 1). A total of 2 μL of 1:100 diluted PCR products labeled with four different dyes (6-FAM, VIC, NED, and PET; Applied Biosystems) were mixed with 8.35 μL of Hi-Di Formamide (Applied Biosystems) and 0.15 μL of GeneScan 500 LIZ Size Standard (Applied Biosystems), and sent to GenoQuebec (Montreal, Canada) for genotype reading on an ABI 3730 genetic analyzer. Results were analyzed with GeneMapper 3.7 software (Applied Biosystems).

Table 1.

Characteristics of 16 microsatellites validated for Thuja occidentalis.

Observed
Locus Primer sequences (5′–3′) GenBank accession no. Dye Repeat motif Size (bp)a Ta (°C) MG A Min Max
TO791 F: AAGAGATTTATTTGCCCTCCG JX475983 VIC (CA)12 141 57 1 16 133 167
R: ATGGTTGATGGACTCCTTGG
TO605 F: GAATAACTTCTTCTGGGAAAGATACA JX475984 PET (AC)8 190 59 1 10 174 196
R: GAGGTGGAAAGAAGTGGATAAAA
TO328 F: CCCGCAACACCTACTTGTCT JX475985 FAM (TACA)7 215 57 1 4 203 215
R: TGCTCCATGTTTGAAGTTGC
TO53 F: AAATGGCCCATAAGCACAAA JX475986 NED (CA)5 184 58 1 6 174 184
R: GGATGTTTCCAGTTGACGGT
TO925 F: TGTGTTTGTGGTGGCTGACT JX475987 FAM (TG)20 151 58 2 22 129 217
R: CATTCATACATTTCCCATCCA
TO727 F: GAGATTCCTTTAAAATATTGGCAT JX475988 VIC (GA)11 241 57 2 14 233 325
R: CCCTCCCATTCCTCTTAATG
TO659 F: TGATGCACCAATTTTCTTTGG JX475989 PET (CT)9 191 56 2 7 181 195
R: TGATGCACTTTAAGGTGTAGGG
TO29 F: TGCAGTGTTAGTGGAGCAACTT JX475990 NED (CA)5 162 57 2 14 148 186
R: TCATTGTTTATTCCCTAAGATGGA
TO737 F: GAGCAAGAAGGAGAGTGGGA JX475991 PET (AGAT)11 124 63 3 6 102 130
R: CCTAGGTTGCCTTGTTGTCC
TO587 F: GTGCCAAACTTTTCAAGGTAAGA JX475992 NED (CT)8 167 62 3 13 139 211
R: GCAAGAGCACAAATGATCACA
TO512 F: TGCATAACAACTCTTCTTAAATCAGC JX475993 FAM (CT)8 194 63 3 11 146 212
R: AGGTCCTATCTAGGTCTTAGACAACTT
TO503 F: CTTGTCCGTCTGACATGTGTTT JX475994 VIC (GA)8 190 55 3 12 138 202
R: CACATAGGTTAAGGGTAGTTTCCT
TO715 F: CATCTACATGGTCGATGATTTAAC JX475995 VIC (AG)10 106 60 4 6 100 110
R: TATCCCAAACCAGCAAAACC
TO521 F: CAAATATGGCACCAATGCCT JX475996 PET (CT)8 121 54 4 17 113 239
R: CAATTTCCTCAGGTTTGGGA
TO418 F: ATGCTTTTCTAACCCTTTTGGA JX475997 NED (AC)7 253 61 4 8 163 255
R: TGATCAGTTGGATTTCTAGATTGC
TO20 F: TTTGGCTTGTAGGTGGTTTT JX475998 FAM (TG)5 192 57 4 15 168 204
R: CTCCATTTTGGAGTGTTGGT

Note: A = number of alleles observed; Max = maximum allele size observed during screening; MG = multiplex group; Min = minimum allele size observed during screening; Ta = annealing temperature.

a

Product size from shotgun pyrosequencing.

All 16 loci showed interpretable, repeatable, and polymorphic patterns (Table 1). We used Multiplex Manager (Holleley and Geerts, 2009) to design and optimize multiplex PCRs to find annealing temperatures for each multiplex group to ensure specific amplifications and avoid complementary sequences among primers. Primer pairs were multiplexed to reduce amplification costs (Table 1). Coamplifications of all multiplexed primers were tested on two populations (30 trees per population) sampled from islands in Lake Duparquet, northwestern Quebec (Table 2). PCR cycles were the same as those mentioned previously, except for multiplexed annealing temperatures (M1 at 57°C, M2 at 56°C, M3 at 55°C, M4 at 54°C). PCR products were genotyped as previously detailed.

Table 2.

Results of initial primer screening in Thuja occidentalis samples from Lake Duparquet, Lake Duparquet Research & Teaching Forest, Quebec, Canada.

Island 58 (N = 30)a Island 134 (N = 30)a
Locus A Ho He FIS Null alleles present (frequency) A Ho He FIS Null alleles present (frequency)
TO53 5.00 0.567 0.705 0.212 no 4.00 0.900 0.652 −0.366 no
TO328 4.00 0.567 0.585 0.048 no 3.00 0.667 0.491 −0.343 no
TO605 3.00 0.200 0.580 0.665* yes (0.24) 2.00 0.367 0.433 0.169 no
TO791 12.00 0.667 0.794 0.177 no 11.00 0.800 0.839 0.063 no
TO29 7.00 0.500 0.543 0.096 no 7.00 0.700 0.712 0.034 no
TO659 4.00 0.400 0.581 0.326 yes (0.11) 6.00 0.500 0.608 0.194 no
TO727 2.00 0.833 0.486 −0.706* no 5.00 0.900 0.686 −0.296 no
TO925 18.00 0.800 0.847 0.072 no 10.00 0.667 0.770 0.151 no
TO503 6.00 0.967 0.644 −0.487* no 4.00 0.633 0.521 −0.199 no
TO512 5.00 0.367 0.322 −0.121 no 7.00 0.733 0.556 −0.305 no
TO587 5.00 1.000 0.712 −0.391* no 7.00 0.867 0.710 −0.204 no
TO737 5.00 0.733 0.634 −0.139 no 4.00 0.867 0.624 −0.375 no
TO20 2.00 0.400 0.320 −0.234 no 4.00 0.933 0.676 −0.366 no
TO418 3.00 0.067 0.065 −0.009 no 3.00 0.433 0.443 0.038 no
TO521 8.00 0.933 0.777 −0.185 no 8.00 0.800 0.738 −0.067 no
TO715 3.00 0.500 0.583 0.159 no 3.00 0.500 0.529 0.072 no
Mean 5.75 0.594 0.574 5.50 0.704 0.624
SE 1.031 0.068 0.050 0.658 0.045 0.030

Note: A = number of alleles; FIS = inbreeding coefficient; He = expected heterozygosity; Ho = observed heterozygosity.

*P ≤ 5%; Bonferroni correction was applied, and indicative adjusted P value for 5% nominal level was 0.0031.

a

Geographical coordinates: Island 58 (48°26′41.4″N, 79°15′51.9″W), Island 134 (48°27′52.5″N, 79°16′19.6″W).

The number of different alleles per locus (A), observed heterozygosity (Ho), and expected heterozygosity (He) were calculated in GenAlEx version 6.2 (Peakall and Smouse, 2006). Inbreeding coefficient (FIS) and Hardy–Weinberg equilibrium (HWE) tests were done in FSTAT version 2.9.3 (Goudet, 2001). Null allele presence was checked in MICRO-CHECKER (Van Oosterhout et al., 2004). Mean values for A, Ho, and He were, respectively, 5.75, 0.594, and 0.574 on Island 58, and 5.50, 0.704, and 0.624 on Island 134 (Table 2). FIS ranged from −0.706 to 0.665 on Island 58, and from −0.357 to 0.194 on Island 134 (Table 2).

CONCLUSIONS

Shotgun pyrosequencing has proved to be effective for isolating microsatellite markers in EWC. The four sets of multiplex microsatellite loci that were developed here for the first time will facilitate future studies of population genetics in EWC, including investigating phylogeographic patterns of postglacial expansion in North America, and studying the impacts of habitat fragmentation on population genetic structure and gene flow. They will also help resolve questions regarding regeneration patterns in this species along postfire successions (Bergeron, 2000).

Appendix 1.

Voucher information for Thuja occidentalis samples. All samples were preserved at the Institut de recherche sur les forêts, Université du Québec en Abitibi-Témiscamingue, Canada.

No. Site Latitude Longitude Location Country Year of collection
1 MZ1 49°52′31.44″N 74°23′34.224″W Chibougamau Canada 2007
2 MZ2 49°54′32.976″N 74°19′21.396″W Chibougamau Canada 2007
3 MZ3 49°57′12.636″N 74°13′44.688″W Chibougamau Canada 2007
4 MZ4 49°38′30.336″N 74°20′2.58″W Chibougamau Canada 2007
5 MZ5 48°55′39.792″N 78°53′8.808″W James Bay Canada 2007
6 MZ6 49°25′23.412″N 79°12′39.492″W James Bay Canada 2007
7 MZ7 49°51′30.708″N 78°36′25.956″W James Bay Canada 2007
8 MZ8 49°53′0.564″N 78°38′45.78″W James Bay Canada 2007
9 MZ9 49°51′21.924″N 78°38′41.496″W James Bay Canada 2007
10 DZ1 48°32′24.72″N 78°38′30.696″W Abitibi Canada 2007
11 DZ2 48°28′12.54″N 79°27′8.46″W Abitibi Canada 2007
12 DZ3 48°28′47.244″N 79°26′12.624″W Abitibi Canada 2007
13 DZ4 48°25′53.796″N 79°24′6.588″W Abitibi Canada 2007
14 DZ5 48°15′6.656″N 78°34′29.208″W Abitibi Canada 2007
15 DZ6 48°25′51.636″N 79°23′2.976″W Abitibi Canada 2007
16 DZ7 48°12′4.752″N 79°25′8.796″W Abitibi Canada 2007
17 CZ1 47°25′45.192″N 78°40′42.528″W Témiscamingue Canada 2007
18 CZ2 47°25′0.084″N 78°40′55.704″W Témiscamingue Canada 2007
19 CZ3 47°23′44.052″N 78°43′53.904″W Témiscamingue Canada 2007
20 CZ4 47°20′2.18″N 79°23′33.396″W Témiscamingue Canada 2007
21 CZ5 47°18′39.96″N 78°30′55.8″W Témiscamingue Canada 2007
22 CZ6 47°27′14.22″N 78°35′15.54″W Témiscamingue Canada 2007
23 CZ7 47°25′8.184″N 78°40′42.384″W Témiscamingue Canada 2007
24 CZ8 47°24′56.844″N 78°42′41.94″W Témiscamingue Canada 2007
25 IS58 48°26′41.4″N 79°15′51.9″W Abitibi Canada 2008
26 IS134 48°27′52.5″N 79°16′19.6″W Abitibi Canada 2008

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