1 2 3 4 5 6 7 8 9 Conservation genetics and genetic mating system of the yellow-shouldered blackbird (Agelaius xanthomus), an endangered island endemic Submitted to Conservation Genetics Irene Liu Duke University Department of Biology irene.a.liu@gmail.com 1 10 Results without Qm10 11 Calculation and comparison of genetic diversity: Summary statistics for genetic 12 diversity across nine loci in the yellow-shouldered blackbird are shown in Table S2a. The 13 bootstrap showed that yellow-shouldered blackbirds had lower allelic diversity, Shannon 14 diversity indices, and expected heterozygosity than any of the red-winged blackbird populations 15 (P ≤ 0.0001 for all measures, Table S2b, Fig. S1). This comparison included the Bahamas 16 population, which itself had significantly lower diversity than that of the continental populations 17 (Fig. S1; Liu et al. in revision). The yellow-shouldered blackbirds also had lower average allelic 18 diversity across loci (5.43 alleles/locus) than the Bahamas red-winged blackbirds (12.71 19 alleles/locus), despite the yellow-shouldered blackbird’s greater raw allelic diversity at Pca3 20 (data not shown). By contrast, the yellow-shouldered blackbirds did not have significantly 21 different levels of inbreeding when compared to the Bahamas red-winged blackbirds (t = 0.87, df 22 = 6, P = 0.42) or with all red-winged blackbird populations (F = 1.03, df = 8, P = 0.43). 23 Estimate of effective population size: Estimates for the LD method in NeEstimator for 24 the yellow-shouldered blackbird are shown in Table 2. Estimated Ne for the Bahama red-winged 25 blackbirds was significantly larger than the values for the yellow-shouldered blackbird (95% 26 confidence intervals did not overlap). Separately, ONeSAMP calculated a mean Ne of 70.2 (95% 27 CI = 61.5, 85.5), while COLONY calculated an Ne of 89 (95% CI = 64, 122) for the yellow- 28 shouldered blackbird. The average estimate of Ne for the yellow-shouldered blackbird was 87.2 29 ±16.2 SD. This quantity ranges from 18-26% of the 2012 pre-breeding census size of 400 birds 30 in southwestern Puerto Rico. 31 Evidence of bottleneck: Under two of three models, BOTTLENECK detected 32 significant heterozygosity excess (higher observed than expected heterozygosity, P < 0.01 for 2 33 both Wilcoxon and sign tests), indicating a recent bottleneck. Whereas the IAM and TPM 34 predicted heterozygosity excess at all nine loci, the SMM predicted heterozygosity deficiency at 35 two loci. Thus, while predicting significance using the Wilcoxon test (P = 0.04), it did not 36 predict significance using the sign test (P = 0.27). BOTTLENECK reported a normal L-shaped 37 distribution for all models, indicating that there was no mode-shift in the allele frequency 38 distribution (i.e., no deviation from allele frequencies predicted by drift-mutation equilibrium). 39 Similar but weaker evidence of a bottleneck was revealed for the Bahamas red-winged 40 blackbird population. Using the sign test, the number of loci showing heterozygosity excess 41 versus heterozygote deficiency was significant under the IAM. Using the Wilcoxon test, the 42 proportion was significant under both the IAM and TPM (all P < 0.02). Predictions under the 43 SMM were not significant in either test. 3 44 45 46 47 48 49 Figure S1 Genetic diversity, omitting Qm10, as measured by allelic diversity, expected heterozygosity, and Shannon diversity estimated from bootstrap simulations for six continental red-winged blackbird (“Cont. RWBL”, black) populations, one island red-winged blackbird (“Bah. RWBL”, black) population, and the yellow-shouldered blackbird (“YSBL”, gray) population. Bootstrap resample size was 20. The yellow-shouldered blackbirds have significantly less genetic diversity than both red-winged blackbird populations 4 50 Table S1. Primers used in the study. L = allele length, n = number of alleles. Locus Aph54 Forward/reverse primer sequences Dye Repeat motif GCTGCTGTCTCTATGTCAC 6-FAM ATT GACACCTTTCACCAGACC LTMR6 GCCATGCCACAGGAGTGAGTC HEX GT AGTCATCTCCATCMGGGCAT Qm10 GGAATTCCAGTATGTGAATGAGTC NED AAT ATTGCAAAAAACAGAAGCATTTTAAC Dpµ16 ACAGCAAGGTCAGAATTAAA 6-FAM AC,GC AACTGTTGTGTCTGAGCCT Pca3 GGTGTTTGTGAGCCGGGG NED GT TGTTACAACCAAAGCGGTCATTTG Ap38 GGAGGGAGACCTCTTAATAC HEX CATC CGACAGAGCTGGTGTCAAAA Ap79 CCACTTCTGCTGAACATAGGG NED AAC GTGCTGCAATTGTGGTCTTG Ap107 GAAACATCCAAACCTGGCTTG 6-FAM AGAT AATGGACGTGCAGCCCTTC Ap144 TCCATAACACAGTTGTCAGAG HEX AGAT CTTACACAGGCACACAAACC L n 165-253 35 GenBank AY928531.1 Reference Westneat and Mays (2005) 183-213 14 FM201465.1 McDonald and Potts (1994) 211-250 16 AF013235.1 Hughes et al. (1998) 150-167 11 AM262982.1 Dawson et al. (1997) 155-179 11 AJ279805.1 Dawson et al. (2000) 268-284 5 JF907496.1 Barker et al. (2011) 218-274 15 JF907499.1 Barker et al. (2011) 207-280 27 JF907500.1 Barker et al. (2011) 187-252 31 JF907502.1 Barker et al. (2011) 5 51 52 53 54 55 56 57 58 Table S2. Summary of population genetics, omitting Qm10. Sample size (N) and means for raw (Na) and effective (Nea) number of alleles, Shannon diversity index (I), observed (Ho) and expected (He) heterozygosity, and inbreeding coefficient (FIS) for (a) eight loci in yellowshouldered blackbirds and (b) seven loci in yellow-shouldered blackbirds (YSBL) and redwinged blackbirds (Liu et al. in revision). Numbers in parentheses are standard error. (a) N 63 YSBL 59 60 61 Na 5.38 (1.21) Nea 3.53 (0.70) I 1.29 (0.18) Ho 0.66 (0.06) He 0.66 (0.05) FIS -0.005 (0.017) (b) N YSBL 63 Bahamas 66 KY 32 MI 51 NY 31 Ontario 13 PA 60 WA 31 WI 22 Na 5.43 (1.39) 12.71 (3.75) 18.29 (2.85) 20.86 (3.12) 16.86 (2.40) 12.14 (1.24) 21.57 (3.62) 15.29 (2.46) 16.43 (2.15) Ne 3.58 (0.81) 7.00 (1.93) 10.85 (1.79) 11.56 (1.91) 10.43 (1.73) 8.13 (1.11) 11.22 (2.11) 9.69 (1.78) 11.06 (1.79) I 1.28 (0.21) 1.87 (0.33) 2.51 (0.19) 2.57 (0.20) 2.46 (0.18) 2.23 (0.14) 2.55 (0.21) 2.36 (0.19) 2.49 (0.17) Ho 0.66 (0.06) 0.74 (0.07) 0.86 (0.02) 0.84 (0.03) 0.83 (0.03) 0.88 (0.04) 0.87 (0.03) 0.83 (0.04) 0.88 (0.04) He 0.65 (0.06) 0.76 (0.07) 0.88 (0.03) 0.89 (0.03) 0.88 (0.03) 0.86 (0.02) 0.89 (0.02) 0.87 (0.03) 0.89 (0.02) FIS -0.004 (0.020) 0.018 (0.018) 0.024 (0.021) 0.054 (0.023) 0.055 (0.022) -0.026 (0.040) 0.012 (0.021) 0.039 (0.021) 0.015 (0.037) 62 6 63 64 65 66 67 Table S3. Estimates of Ne, omitting Qm10, in the yellow-shouldered blackbird (YSBL) vs. redwinged blackbird populations using the LD method in NeEstimator. 95% confidence intervals are calculated using the jackknife on loci method. Ne in YSBL was estimated using eight loci, while Ne in RWBL was estimated using nine loci. Lowest allele frequency: YSBL Bahamas KY MI NY Ontario PA WA WI 0.05 Ne 80.9 343.1 926.1 Infinite 449.2 Infinite 242.1 141.4 100.5 CI Ne 42.5, 261.2 108.6 125.2, infinite 445.2 88.7, infinite Infinite 236.6, infinite Infinite 77.2, infinite 444.6 83.6, infinite Infinite 122.1, 1942.3 719.3 57.1, infinite 236.8 39.6, infinite 193.9 0.01 CI 55.4, 461.7 192.0, infinite 719.3, infinite 775.9, infinite 168.0, infinite Infinite, infinite 307.1, infinite 115.6, 8570.3 85.9, infinite 68 7 69 70 71 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 Table S4. Microsatellite ascertainment bias is not an issue, shown by effective allelic diversity (Nea) for each of the eight loci that were amplified in both red-winged blackbird (RWBL) and yellow-shouldered blackbird (YSBL). The Ontario population was excluded when calculating the mean allelic diversity of the continental populations (in bold), because lower measurements in Ontario almost certainly stem from missed alleles and would have artificially increased the distribution about the mean. Differences in allelic diversity between the two species are indeed larger in the RWBL-derived loci than the loci derived from other species. However, YSBL have the lowest allelic diversity across six loci, indicating the signal of lower diversity is not an artefact of species-specific polymorphism. The two exceptions are LTMR6 and Qm10, two non-RWBL-derived loci, where the Bahamas RWBL population has the lowest allelic diversity. Furthermore, at five other loci, both the YSBL and the Bahamas RWBL population have estimated levels of allelic diversity falling outside the mean ± SD of the continental populations. These results suggest the markers are detecting true variation within and across species, and that this variation can be reliably identified and compared with a closely related species. Populations with similar sample sizes are highlighted. These populations show the same trend that the YSBL have lower allelic diversity at all loci but Qm10. N KY 32 MI 51 NY 31 Ontario 13 PA 60 WA 31 WI 22 Mean_excl_Ont SD_excl_Ont Bahamas YSBL 66 63 RWBL-derived loci Non-RWBL-derived loci Aph54 Ap107 Ap144 Ap79 LTMR6 Qm10 Dpu16 Pca3 16.38 13.47 16.25 8.94 9.99 8.19 6.94 3.94 16.21 16.11 16.83 10.49 10.42 6.76 6.98 3.86 15.38 10.22 16.86 10.74 9.56 7.84 6.28 4.00 12.52 10.24 9.14 8.45 7.19 4.69 5.73 3.63 16.71 16.33 17.73 8.94 8.77 8.96 5.31 4.73 15.75 13.93 13.73 6.77 6.24 6.99 7.88 3.53 18.26 12.41 15.37 9.31 10.30 8.27 7.39 4.38 15.89 13.24 15.13 9.09 8.93 7.39 6.64 4.01 1.62 2.30 2.72 1.23 1.51 1.30 0.85 0.39 14.21 4.59 11.34 7.89 11.27 3.55 4.87 2.00 2.39 2.92 2.88 8.47 2.92 2.20 2.00 1.90 89 8 90 91 92 93 94 95 96 97 98 99 100 101 102 103 104 105 106 107 108 109 110 111 References Barker FK, Bell JJ, Bogdanowicz SM, Bonatto SL, Cezilly F, Collins SM, Dubreuil C, Dufort MJ, Eraud C, Fuseya R, Heap EA, Jacobsen N, Madders M, McEwing R, Michel AP, Mougeot F, Ogden RS, Orantes LC, Othman AS, Parent É, Pulido-Santacruz P, Rioux-Paré R, Roberts MF, Rosazlina R, Sakamoto T, De-León PS, Sévigny J-M, St-Onge P, Terraube J, Tingay RE, Tremblay R, Watanabe S, Wattier RA (2011) Permanent genetic resources added to Molecular Ecology Resources Database 1 June 2011–31 July 2011. 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