Article (refereed)
Hernandez, G.; Buonamici, A.; Walker, K.; Vendramin, G.
G.; Navarro, C.; Cavers, S.. 2008 Isolation and
characterization of microsatellite markers for Cedrela
odorata L. (Meliaceae), a high value neotropical tree.
Conservation Genetics, 9, 2. 457-459.
doi:10.1007/s10592-007-9334-y
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Isolation and characterization of microsatellite markers for Cedrela odorata L.
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(Meliaceae), a high value neotropical tree.
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Running title (45 chars): Microsatellites for Cedrela odorata
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Hernandez G1,2, Buonamici A3, Walker K2, Vendramin GG3, Navarro C1 and Cavers S2,*
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Rica
Centro Agrónomico Tropical de Investigación y Enseñanza, Cartago, Turrialba 7170, Costa
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Midlothian EH26 0QB, Scotland, UK
NERC Centre for Ecology and Hydrology, CEH Edinburgh, Bush Estate, Penicuik,
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(Florence), Italy.
Plant Genetics Institute, Consiglio Nazionale delle Ricerche (CNR), 50019 Sesto Fiorentino
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*
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Hydrology Edinburgh, Bush Estate, Penicuik, Midlothian EH26 0QB, Scotland, UK. Tel. +44
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131 445 4343, Fax. +44 131 445 3943, Email scav@ceh.ac.uk
To whom correspondence should be addressed: Dr S Cavers, Centre for Ecology and
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Keywords (5): Cedrela odorata, Cedar, Meliaceae, microsatellites
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Abstract (82 words)
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We describe 9 primers for amplification of microsatellite loci for the Neotropical tree Cedrela
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odorata L. (Meliaceae). Loci were isolated from an enriched library derived from a single
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DNA sample from a tree in Costa Rica. Levels of polymorphism were determined using
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samples from a large progeny trial. Across loci, the number of alleles ranged from 14 to 30.
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Observed heterozygosity levels ranged from 0.61 to 0.88. No linkage disequilibria were
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detected although some departures from HWE were found, probably due to a Wahlund effect.
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Cedrela odorata (Meliaceae), known as Cedro Amargo or Spanish Cedar, is a high-value
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species of the Mahogany family, widely distributed in the neotropics (Holdridge et al. 1997).
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Internationally valued for its high quality wood, C. odorata has been used for construction,
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furniture and boat building amongst other things (Cordero and Boshier 2003). As a result,
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heavy selective logging has severely reduced wild populations, to the point that the species is
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now threatened at a provenance level (Patiño 1997).
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Previous studies have assessed genetic structure using AFLP and universal chloroplast DNA
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markers (Cavers et al 2003a,b) and quantitative traits (Navarro et al. 2005), thoroughly
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describing genetic variation in the species at a landscape scale in Mesoamerica. Now,
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attention is turning to restoration efforts and best practice for sourcing seed. A major progeny
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trial is now underway in Costa Rica to examine the effects of landscape context on progeny
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fitness, as recent studies have shown that alteration of the forest surrounding seed trees
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changes gene flow patterns (e.g. Rocha and Aguilar, 2001), with potentially significant
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consequences for inbreeding rates in progeny arrays. To enable analysis of mating system
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variation in these progeny arrays, a set of microsatellites were isolated for C. odorata. Loci
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were optimised for PCR and screened for polymorphism using 487 individuals in 68 families,
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from 12 populations distributed across Mesoamerica.
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DNA was extracted from silica-gel-dried leaf material (DNeasy Plant mini kit, QIAGEN)
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from a single adult tree of C. odorata from Costa Rica. A microsatellite library enriched for
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di- (AG, GT, AT, GC) and trinucleotide (CAA, ATT, GCC) repeats was constructed
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following Edwards et al. (1996). The enriched DNA was cloned into pGEM-T vector and
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transformed into JM109 cells. A total of 200 clones were sequenced with an Amersham
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MegaBACE 1000 automated sequencer using DYEnamic ET Terminator Sequencing Kit
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(Amersham Biosciences).
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Screening for polymorphism and optimisation of PCR conditions was carried out using leaf
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material from families from different, widely-separated provenances (Tulum and Xpujil,
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Mexico; Cedros, Honduras; Hojancha, Costa Rica) to maximise the potential for detection of
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polymorphism. All microsatellites were amplified using 25.0 ul PCR reactions consisting of
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the following: 2.0 ul template DNA, 15.4 ul H2O, 2.0 ul primers, 2.5 ul 10X buffer, 0.5 ul
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dNTPs, 0.4 ul BSA, 0.2 ul Taq DNA polymerase (New England Biolabs). Reactions were run
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on a Hybaid MBS thermocycler to the following protocol: 1 min at 94 °C, then 30 cycles of
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60 s at 94 °C, 60 s at 55 °C, 60 s at 72 °C and finally 5 min at 72 °C. Optimal PCR reaction
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conditions for each of the polymorphic pairs were determined by testing a range of annealing
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temperatures (55.0 -70.3 °C) and different template DNA concentrations (1:5, 1:10, 1:20 and
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1:1). In all cases the forward primer was labelled with either IRD 700 or 800 fluorescent label
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(MWG Biotech). PCR products were then separated on 6% polyacrylamide gel (25 cm), and
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visualized using a LI-COR 4200 IR2 automated genotyper. PCR products were run out
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alongside a microSTEP DNA size standard (Microzone Limited) and fragment sizes were
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scored using SAGA™ software. Numbers of alleles were calculated, and observed and
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expected heterozygosity, exclusion probability (Cervus v3.0, Marshall et al 1998) and null
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allele rate were estimated (Microchecker v2.2.3, van Oosterhout et al. 2004). Tests for Hardy-
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Weinberg equilibrium (HWE) and linkage disequilibrium, corrected for multiple comparisons
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and considering 1 individual per family, were carried out using Genepop v3.3 (Raymond &
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Rousset 1995). Results for effective numbers of alleles (NA), observed (HO) and expected
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heterozygosity (HE) are reported (Table 1) for the collection as a whole and for a single
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population (Tikal) to demonstrate the within-population utility of the markers.
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In 80% of the sequences a microsatellite motif was detected. However, about 130 sequences
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were discarded because of unfavourable properties for primer design. In 30 cases primers
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were designed, using PRIMER 3 software (Rozen & Skalestky 2000). Of these, 9 gave clear,
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interpretable band patterns and were polymorphic (Table 1). The numbers of alleles per locus
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ranged from 14 to 30 with levels of observed heterozygosity from 0.61 to 0.88. Null alleles
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were detected at rates of >0.05 at ced41, ced61a, ced65 and ced131. In all cases, these are
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most likely due to scoring errors due to stuttering, as indicated by low frequencies of
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heterozygote genotypes with size differences of a single repeat unit (van Oosterhout et al.
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2004). Across the whole dataset, only loci ced2 and ced44 showed no departure from HWE.
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For some loci, this was contributed to by the presence of null alleles (highest null allele
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frequency estimated at locus ced61a with 18.1%, Table 1), but most probably reflects a
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heterozygote deficiency due to combination of samples from several, widely-distributed
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populations (Wahlund effect). No linkage disequilibria between loci (P > 0.05) were
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observed, suggesting that these loci should be valuable markers for population genetics and
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parentage analysis for Cedrela odorata.
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References
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Cavers S, Navarro C, Lowe AJ (2003)a A combination of molecular markers identifies
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evolutionarily significant units in Cedrela odorata L. (Meliaceae) in Costa Rica. Conserv
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Genet 4:571-580
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Cavers S, Navarro C, Lowe AJ (2003)b Chloroplast DNA phylogeography reveals
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colonization history of a Neotropical tree, Cedrela odorata L. (Meliaceae) in Mesoamerica.
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Molec Ecol 12:1451-1460
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1
Cordero J, Boshier DH (2003) Árboles de Centroamérica: un manual para extesionistas.
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Oxford Forestry Institute, UK. CATIE, Turrialba, CR.
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Holdridge LR, Poveda LJ, Jiménez Q (1997) Árboles de Costa Rica. San José, CR. Centro
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Científico Tropical. v. 1, p. 269
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Marshall TC, Slate J, Kruuk LEB, Pemberton JM (1998) Statistical confidence for likelihood-
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based paternity inference in natural populations. Molec Ecol 7: 639–655
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Navarro C, Cavers S, Pappinen A, Tigerstedt P, Lowe AJ, Merilä J (2005) Contrasting
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Quantitative Traits and Neutral Genetic Markers for Genetic Resource Assessment of
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Mesoamerican Cedrela odorata. Silvae Genet 54(6): 281-292
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Patiño F (1997) Genetic resources of Swietenia and Cedrela in the Neotropics. United
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Nations Food and Agriculture Organization. Rome, Italy.
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Raymond M, Rousset F (1995) genepop (Version 1.2): Population genetics software for exact
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tests and ecumenicism. J Hered 86: 248–249
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Rocha OJ, Aguilar G (2001). Variaton in the breeding behaviour of the dry forest tree
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Enterolobium cyclocarpum (Guanacaste) in Costa Rica. Am J Bot 88: 1600-1606
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Rozen S, Skaletsky H (2000) Primer3 on the WWW for general users and for biologist
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programmers. In: Krawetz S, Misener S (eds) Bioinformatics Methods and Protocols:
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Methods in Molecular Biology. Humana Press, Totowa, NJ, pp 365-386
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Van Oosterhout C, Hutchinson WF, Wills DPM, Shipley P (2004) Micro-Checker : software
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for identifying and correcting genotyping errors in microsatellite data. Molec Ecol Notes 4:
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535-538
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Acknowledgements
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This work was part of the project SEEDSOURCE, funded by the EC under FP6 INCO
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(contract 003708). Library development, cloning and sequencing was done by CNR and
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optimisation at CEH by GH during his M.Sc., sponsored by CATIE and Ministerio de Ciencia
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y Tecnología.
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Table 1. Primer sequences, characterisation and basic descriptive statistics of 9 microsatellite markers isolated from Cedrela odorata.
Locus
Array
Primer Sequences (5' - 3')
Ced2
(GA)20
F:TTTGCTTTGAGAAACCTTGT*
R:AACTTTCGAATTGGTTAAGG
F:CAAAGACCAAGATTTGATGC*
R:ACTATGGGTGGCACAACTAC
F:TCATTCTTGGATCCTGCTAT*
R:GTGGGAAAGATTGTGAAGAA
F:ACTCCATTAACTGCCATGAA*
R:ATTTTCATTCCCTTTTAGCC
F:GATCTCACCCACTTGAAAAA*
R:GCTCATATTTGAGAGGCATT
F:CAATCAAACCAAAAATGGAT*
R:GCAAATTAACCAGAAAAACG
F:GAGTGAGAAGAAGAATCGTGATAGC*
R:GAGGTTCGATCAGGTCTTGG
F:ATTTTCATTCCCTTTTAGCC*
R:TTATCATCTCCCTCACTCCA
F:CTCGTAATAATCCCATTCCA*
R:GGAGATATTTTTGGGGTTTT
Allele
Size / bp
T (°C)
130-170
55
N
NA
HO
HE
Pr
(Ex1)
Pr
(Ex2)
Null
rate
400 19
0.850
0.882
0.614 0.762
0.017
(63) (12) (0.841) (0.842)
Ced18
(GA)23
130-150
55
403 19
0.797
0.844
0.545 0.708
0.029
(69) (16) (0.826) (0.875)
Ced41
(TC)18
120-160
55.5
451 21
0.745
0.910
0.693 0.819
0.100
(72) (12) (0.792) (0.839)
Ced44
(TG)14(AG)17
180-240
55.5
456 30
0.882
0.931
0.755 0.860
0.028
(74) (17) (0.959) (0.920)
Ced54
(GA)15(AG)6G(GA)5
120-160
55
408 28
0.843
0.936
0.772 0.871
0.053
(70) (21) (0.886) (0.931)
Ced61a (TG)10
240-270
55.5
428 14
0.605
0.868
0.581 0.737
0.181
(71) (10) (0.535) (0.843)
Ced65
(GA)7(CA)14
160-200
55.5
468 17
0.618
0.802
0.456 0.632
0.136
(76) (12) (0.605) (0.798)
Ced95
(CT)17(AC)13
190-250
55
389 28
0.918
0.829
0.715 0.834
0.043
(63) (18) (0.905) (0.913)
Ced131 (CT)16
80-120
55
419 14
0.745
0.829
0.507 0.677
0.053
(66) (10) (0.773) (0.823)
Total cumulative exclusion probabilities
0.999 0.999
* Indicates fluorescently labelled primer. Abbreviations are: number of individuals (N), number of alleles (NA), observed (HO) and expected (HE) heterozygosities and
exclusion probability Pr(Ex - for first parent 1 and second parent 2). Values in brackets for N, NA, HO, HE are single-population estimates from the population Tikal.
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GenBank
Accession
no.
EF413962
EF413963
EF413964
EF413965
EF413966
EF413967
EF413968
EF413969
EF413970