Abstract
We identified 20 novel polymorphic microsatellite markers for use in South Island robins (Petroica australis). Markers were isolated from clones enriched for microsatellite repeats, and using 454 pyro-sequencing. South Island robins, like many New Zealand endemic species, have relatively low microsatellite diversity. Alleles per locus ranged from 2 to 7 (mean 3.00, SE 0.299). Mean expected heterozygosity was 0.436 (SE 0.047). Markers were amplified using cost-effective universal fluorescent labeling in multiplex PCR and will be useful in conservation genetics research involving this locally threatened species.
Avoid common mistakes on your manuscript.
The South Island robin (Petroica australis) is a small forest passerine native to New Zealand and includes the subspecies P. a. rakiura on Stewart Island (Higgins and Peter 2002; Miller and Lambert 2006). Although classified as a species of least concern (IUCN 2011), robins are locally threatened by introduced predators, and the Stewart Island subspecies is listed as ‘Nationally Vulnerable’ (Higgins and Peter 2002; Miskelly et al. 2008). On Stewart Island, population declines prompted the translocation of 25 individuals in 2000 to Ulva Island, an open sanctuary established by the Department of Conservation and Ulva Island Trust. This population is closely monitored and represents an opportunity to study a small, wild bird population for which a high quality pedigree has been constructed (Jamieson 2010). An informative set of neutral markers will complement the pedigree for use in conservation genetics studies of South Island robins aimed at better understanding the genetic consequences of bottlenecks, small population size and inbreeding (Jamieson 2010).
Ten microsatellite loci, originally developed for use in other species, were previously identified as polymorphic in South Island robins, including those on Ulva Island (Boessenkool et al. 2007). Increasing the number of markers will offset low genetic diversity typical of this and other New Zealand native birds.
We prepared a library enriched for dinucleotide STRs (GA)12 and (GT)12 using DNA extracted from two South Island robins following the methods of Glenn and Schable (2005). We sequenced positive clones using an ABI 3730 Genetic Analyser (Applied Biosystems) and edited sequences using Sequencher v3.7. We also isolated microsatellites using shotgun sequencing scaled to 1/8th of a run on the Roche 454 GS-FLX System (Roche, Penzberg, Germany) following the methods of Abdelkrim et al. (2009). Reads were screened for di-, tri and tetranucleotide microsatellite repeats using MsatCommander v0.8.1 (Faircloth 2008). Primers were design for sequences obtained from both methods using Primer3Plus (Untergasser et al. 2007). We appended forward primers with M13 sequence (5′-TGTAAAACGACGGCCAGT-3′) at the 5′ end to facilitate the use of universal dye labeled primers as described in Schuelke (2000) and added PIG-tails (5′-GTTTCTT-3′) to the 5′ end of reverse primers to improve scoring (Brownstein et al. 1996). Additional information about clone screening and read yields from 454-sequencing can be found in the supplementary material (Online Resource ESM_1).
We screened loci for polymorphism initially using simplex PCR in 12 to 24 individuals, assigning polymorphic loci to multiplex groups with the aid of Multiplex Manager v1.1 (Holleley and Geerts 2009). Online supplemental material contains details on multiplex grouping, repeat motifs and the assignment of these loci to homologous locations in the zebra finch genome following Olano-Marin et al. (2010) (Online Resource ESM_1). For PCR amplification, Multiplex PCR was carried out in 384-well plates containing 10 ng of DNA dried into wells at room temperature prior to PCR set-up. Each 2 μl reaction contained 1 μl Type-it Master Mix (QIAGEN), 1 μl primer mix containing forward (0.04 μM) and reverse (0.16 μM) locus-specific primers and M13-tagged fluorescent dyes (6-FAM, VIC, NED, PET) (0.16 μM × number of loci) (Schuelke 2000).
Thermocycling conditions were 95°C for 15 min, followed by a touchdown sequence comprising 94°C for 30 s, annealing for 90 s and extension at 72°C for 60 s. Annealing temperature started at 60°C and reduced 1 degree per cycle for 8 cycles. This was followed by 25 cycles at 94°C for 30 s, 52°C for 90 s and 72°C for 60 s with a final 30 min hold at 60°C.
Following PCR amplification, fragment sizes were resolved on an ABI 3730 Genetic Analyser (Applied Biosystems) with GeneScan 500 (LIZ)tm size standard and scored using Genemapper v4.1 (Applied Biosystems). Genemapper scores were visually confirmed and ambiguous scores omitted. Expected and observed heterozygosities were calculated using the GenAlEx v6.41 (Peakall and Smouse 2006) extension for Microsoft Excel 2011. Deviation from Hardy–Weinberg equilibrium was calculated using GenePop v4.0.10 (Raymond and Rousset 1995; Rousset 2008). Data were checked for evidence of null alleles and scoring errors with Micro-Checker v2.2.3 (van Oosterhout et al. 2004) and for linkage between pairs of loci using genotyping data from 2007 (n=31), 2008 (n=30) and 2009 (n=45) separately with GenePop (Raymond and Rousset 1995; Rousset 2008).
Of the 69 loci screened, 20 were used to genotype 275 birds from Ulva Island (Table 1). Alleles per locus ranged from 2 to 7 (mean 3.00, SE 0.299) and mean expected heterozygosity was 0.436 (SE 0.047). After sequential Bonferroni correction (Holm 1979), Pau09 showed deviations from Hardy–Weinberg equilibrium, however, we found no evidence of null-alleles. No locus pairs showed evidence of significant linkage disequilibrium across the 3 years examined. Two additional polymorphic loci, Pau20 (GenBank accession number JQ289044) and Pau23 (JQ289045), failed to amplify well in our multiplex groups using M13 primers but sequence information is available online (http://www.ncbi.nlm.nih.gov/genbank/).
The markers described here will be used in conservation genetics studies of South Island robins and would be candidates for screening in other New Zealand passerines.
References
Abdelkrim J, Robertson BC, Stanton J-A, Gemmell N (2009) Fast, cost-effective development of species-specific microsatellite markers by genomic sequencing. Biotechniques 46:185–192. doi:10.2144/000113084
Boessenkool S, Taylor SS, Tepolt CK, Komdeur J, Jamieson IG (2007) Large mainland populations of South Island robins retain greater genetic diversity than offshore island refuges. Conserv Genet 8:705–714. doi:10.1007/s10592-006-9219-5
Brownstein MJ, Carpten JD, Smith JR (1996) Modulation of non-templated nucleotide addition by Taq DNA polymerase: primer modifications that facilitate genotyping. Biotechniques 20:1004–1010
Faircloth BC (2008) Msatcommander: detection of microsatellite repeat arrays and automated, locus-specific primer design. Mol Ecol Resour 8:92–94. doi:10.1111/j.1471-8286.2007.01884.x
Glenn TC, Schable NA (2005) Isolating microsatellite DNA loci. Methods Enzymol 395:202–222
Higgins PJ, Peter JM (2002) Handbook of Australian, New Zealand and Antarctic birds. Volume 6: pardalotes to shrike-thrushes. Oxford University Press, Melbourne
Holleley C, Geerts P (2009) Multiplex Manager 1.0: a cross-platform computer program that plans and optimizes multiplex PCR. Biotechniques 46:511–517. doi:10.2144/000113156
Holm S (1979) A simple sequentially rejective multiple test procedure. Scand J Stat 6:65–70
IUCN (2011) IUCN red list of threatened species. Version 2011.2. http://www.iucnredlist.org. Accessed 17 Nov 2011
Jamieson IG (2010) Founder effects, inbreeding, and loss of genetic diversity in four avian reintroduction programs. Conserv Biol 25:115–123. doi:10.1111/j.1523-1739.2010.01574.x
Miller HC, Lambert DM (2006) A molecular phylogeny of New Zealand’s Petroica (Aves: Petroicidae) species based on mitochondrial DNA sequences. Mol Phylogen Evol 40:844–855. doi:10.1016/j.ympev.2006.04.012
Miskelly CM, Dowding JE, Elliot GP, Hitchmough RA, Powlesland RG, Robertson HA, Sagar PM, Scofield RP, Taylor GA (2008) Conservation status of New Zealand birds, 2008. Notornis 55:117–135
Olano-Marin J, Dawson DA, Girg A, Hansson B, Ljungqvist M, Kempenaers B, Mueller JC (2010) A genome-wide set of 106 microsatellite markers for the blue tit (Cyanistes caeruleus). Mol Ecol Resour 10:516–532. doi:10.1111/j.1755-0998.2009.02777.x
Peakall R, Smouse PE (2006) Genalex 6: genetic analysis in excel. Population genetic software for teaching and research. Mol Ecol Notes 6(1):288–295. doi:10.1111/j.1471-8286.2005.01155.x
Raymond M, Rousset F (1995) GenePop (version-1.2): population-genetics software for exact tests and ecumenicism. J Hered 86:248–249
Rousset F (2008) GenePop’007: a complete re-implementation of the GenePop software for Windows and Linux. Mol Ecol Resour 8:103–106. doi:10.1111/j.1471-8286.2007.01931.x
Schuelke M (2000) An economic method for the fluorescent labeling of PCR fragments. Nat Biotechnol 18:233–234
Untergasser A, Nijveen H, Rao X, Bisseling T, Geurts R, Leunissen JAM (2007) Primer3Plus, an enhanced web interface to Primer3. Nucleic Acids Res 35:W71–W74. doi:10.1093/nar/gkm306
van Oosterhout C, Hutchinson WF, Wills DPM, Shipley P (2004) Micro-checker: software for identifying and correcting genotyping errors in microsatellite data. Mol Ecol Notes 4:535–538
Acknowledgments
This work was carried out under permits from Environmental Protection Authority (GMD002754) and Otago University Animal Ethics Committee. Funding was provided by Landcare Research, University of Otago, Marsden Fund Council, Department of Conservation, Royal Forest & Bird Protection Society and a Commonwealth Scholarship to S.M.T.
Author information
Authors and Affiliations
Corresponding author
Electronic supplementary material
Below is the link to the electronic supplementary material.
Rights and permissions
About this article
Cite this article
Townsend, S.M., King, T.M. & Jamieson, I.G. Isolation and characterisation of microsatellite markers from the South Island robin (Petroica australis). Conservation Genet Resour 4, 633–636 (2012). https://doi.org/10.1007/s12686-012-9610-0
Received:
Accepted:
Published:
Issue Date:
DOI: https://doi.org/10.1007/s12686-012-9610-0