| Literature DB >> 20650000 |
Joshua M Hull1, David P Mindell, Sandra L Talbot, Emily H Kay, Hopi E Hoekstra, Holly B Ernest.
Abstract
BACKGROUND: Phenotypic and molecular genetic data often provide conflicting patterns of intraspecific relationships confounding phylogenetic inference, particularly among birds where a variety of environmental factors may influence plumage characters. Among diurnal raptors, the taxonomic relationship of Buteo jamaicensis harlani to other B. jamaicensis subspecies has been long debated because of the polytypic nature of the plumage characteristics used in subspecies or species designations.Entities:
Mesh:
Substances:
Year: 2010 PMID: 20650000 PMCID: PMC2927923 DOI: 10.1186/1471-2148-10-224
Source DB: PubMed Journal: BMC Evol Biol ISSN: 1471-2148 Impact factor: 3.260
Sampling locations and the number of individuals for B. j. calurus, B. j. borealis, B. j. harlani, and B. jamaicensis spp (melanistic).
| Subspecies | Location | N |
|---|---|---|
| central California | 68 | |
| Idaho | 35 | |
| Nevada/Utah | 39 | |
| southern California | 36 | |
| Alberta | 2 | |
| Colorado | 11 | |
| Kentucky | 9 | |
| Michigan | 5 | |
| north Texas | 9 | |
| Wisconsin | 33 | |
| Anchorage, Alaska | 6 | |
| Fairbanks, Alaska | 3 | |
| Kuskokwim, Alaska | 10 | |
| Palmer, Alaska | 4 | |
| Kluane, Yukon Territory | 1 | |
| central California | 21 |
Genetic diversity indices for microsatellite and mitochondrial sequence data.
| Nμsat | HO ± sd | Aa ± sd | Ap | Ar | Nmt | HN | HP | π | Hd | |
|---|---|---|---|---|---|---|---|---|---|---|
| 178 | 0.68 ± 0.01 | 14.2 ± 10.3 | 34 | 6.9 | 122 | 14 | 8 | 0.0019 | 0.57 ± 0.003 | |
| central California | 68 | 0.68 ± .01 | 11.4 ± 7.6 | 9 | 6.3 | 29 | 6 | 2 | 0.0012 | 0.43 ± 0.11 |
| Idaho | 35 | 0.66 ± 0.02 | 10.1 ± 6.3 | 5 | 6.5 | 34 | 6 | 2 | 0.0012 | 0.37 ± 0.10 |
| Nevada/Utah | 39 | 0.71 ± 0.02 | 11.2 ± 7.2 | 9 | 6.8 | 29 | 8 | 1 | 0.0016 | 0.57 ± 0.11 |
| southern California | 36 | 0.65 ± 0.02 | 9.6 ± 5.1 | 3 | 6.5 | 30 | 4 | 0 | 0.0009 | 0.35 ± 0.10 |
| 69 | 0.73 ± 0.01 | 12.1 ± 7.9 | 11 | 7.1 | 52 | 13 | 8 | 0.0019 | 0.520 ± .007 | |
| Alberta | 2 | 0.79 ± 0.07 | 2.9 ± 1.1 | 0 | --- | --- | --- | --- | --- | --- |
| Colorado | 11 | 0.73 ± 0.03 | 7.1 ± 3.4 | 1 | 6.6 | 6 | 1 | 0 | --- | --- |
| Kentucky | 9 | 0.72 ± 0.04 | 6.2 ± 2.5 | 0 | --- | 10 | 5 | 1 | 0.0022 | 0.67 ± 0.16 |
| Michigan | 5 | 0.76 ± 0.05 | 5.1 ± 2.0 | 1 | --- | 5 | 3 | 1 | 0.0023 | 0.70 ± 0.22 |
| north Texas | 9 | 0.73 ± 0.04 | 6.7 ± 3.4 | 1 | --- | 5 | 2 | 1 | 0.0008 | 0.33 ± 0.22 |
| Wisconsin | 33 | 0.73 ± 0.02 | 9.8 ± 5.3 | 5 | 6.6 | 26 | 8 | 5 | 0.0022 | 0.47 ± 0.12 |
| 24 | 0.69 ± 0.03 | 9.0 ± 5.3 | 5 | 6.9 | 24 | 5 | 0 | 0.016 | 0.59 ± 0.05 | |
| melanistic migrants | 21 | 0.68 ± 0.03 | 9.0 ± 5.2 | 1 | 6.9 | --- | --- | --- | --- | --- |
Key: Nμsat = the number of samples for which microsatellite data was collected, HO = observed heterozygosity, Aa = average number of alleles per locus, Ap = number of private alleles, Ar = allelic richness averaged across 17 loci, Nmt = the number of samples for which sequence data was collected, HN = the number of haplotypes, HP = the number of private haplotypes, π = nucleotide diversity, Hd = haplotype diversity.
Figure 1Unrooted UPGMA clustering tree based on microsatellite allele frequency differences. Only breeding sites with greater than 20 individuals were included; we assessed support using 10,000 bootstrapped data sets. Nodes with greater than 50% bootstrap support are indicated. The results shown here are consistent with previous research that found support in UPGMA clustering for a distinction between B. j. calurus and B. j. borealis breeding and migration sites [22].
Microsatellite pairwise θST comparisons between B. jamaicensis subspecies.
| ---------- | ||||
| 0.004 | ---------- | |||
| 0.023* | 0.012* | ---------- | ||
| 0.023* | 0.020* | 0.004 | ---------- |
Key: *'s indicate significant differences following Bonferroni correction. Melanistic individuals were sampled during autumn migration within the range of B. j. calurus; however the sample may include individuals that originated outside the range of B. j. calurus.
Figure 2Map of North American . We collected all samples from breeding sites during the breeding season from either young in nests or territorial adults. We collected samples from sites 1-4 within the breeding range of B. j. calurus; samples from sites 5-9 within the breeding range of B. j. borealis; samples from site 10 within the breeding range of B. j. harlani; and we collected the pooled samples from site 11 from migrants of unknown breeding origin, all samples from site 11 appeared phenotypically similar to typical or melanistic B. j. calurus. Sampling areas are shown with associated frequencies of mitochondrial control region haplotypes.
Mitochondrial pairwise ΦST comparisons between B. jamaicensis subspecies
| ---------- | |||
| 0.032* | ---------- | ||
| 0.203* | 0.059* | ---------- |
Key: *'s indicates significant differences following Bonferroni correction.
Figure 3Neighbor joining distance mid-point rooted minimum evolution tree of . Branch length indicates degree of genetic differentiation. Bootstrap values providing > 50% support for nodes are indicated. Gray circles indicate haplotypes sampled from breeding sites of B. j. calurus, white triangles indicate haplotypes sampled from breeding sites of B. j. borealis, black squares indicate haplotypes sampled from breeding sites of B. j. harlani, and asterisks indicate haplotypes that were sampled from migrant hawks in California with plumage consistent with B. j. calurus. We applied midpoint rooting, employing the close-neighbor interchange algorithm for finding the tree, beginning with an initial neighbor-joining tree.
Figure 4Results of full model migration matrix. We allowed all parameters to vary independently. We calculated migration direction and rates from: (A) 17 microsatellite loci and (B) mtDNA control region data. Nm and Nm = estimate for number of migrants/females per generation based on nuclear microsatellites and mtDNA, respectively. Θ = population size (4Neμ; see text). 95% confidence intervals for parameter values are in parentheses. Arrow thickness is proportionate to estimated levels of gene flow (thicker arrows indicate higher relative gene flow).
Mc1r polymorphism for breast color morphs in B. j. calurus and B. j. harlani subspecies.
| Phenotype | Subspecies | Specimen no. | 73 | 292 | 346 |
|---|---|---|---|---|---|
| Rufous | 10094 | . | . | . | |
| Rufous | 13424 | . | . | . | |
| Rufous | 13642 | . | . | . | |
| Rufous | 13651 | . | . | . | |
| Rufous | 13662 | . | . | . | |
| Rufous | 13737 | . | . | . | |
| Rufous | 13775 | . | . | . | |
| Rufous | 13826 | . | . | . | |
| Dark | 11071 | . | . | . | |
| Light | 10101 | G/A | . | . | |
| Light | 11056 | . | . | . | |
| Light | 13670 | . | . | . | |
| Light | 13671 | . | . | . | |
| Light | 13672 | . | C/T | . | |
| Light | 13673 | . | . | C/T | |
| Light | 13674 | G/A | . | . | |
| Partial albino | 6161 | . | . | . | |
| Harlan's | 10983 | . | . | . | |
| Harlan's | 13654 | . | C/T | . | |
| Harlan's | 14133 | . | . | C/T | |
| Harlan's | 14134 | . | . | . | |
| Harlan's | 14138 | . | . | . | |
| Harlan's | 14139 | . | . | . | |
| - | - | - | |||
Key: The nucleotide position and base for the consensus sequence is listed across the top. Amino acids from the hawk consensus sequence are listed below. No amino acid replacements were observed.