| Literature DB >> 36078012 |
Wenshuang Bao1,2, Atul Kathait3, Xiang Li1,2, Kiyoaki Ozaki4, Yukihiro Hanada5, Alexander Thomas6, Geoffrey John Carey7, Jun Gou8, Batmunkh Davaasuren9, Makoto Hasebe10, Paul Ian Holt11, Lukas Pelikan12, Zhongyong Fan13, Siyu Wang13, Xiaoying Xing1,2.
Abstract
The critically endangered Yellow-breasted Bunting has undergone population collapse globally because of illegal hunting and habitat deterioration. It was listed as critically endangered (CR) by the International Union for Conservation of Nature (IUCN) in 2017 and designated a Class I (highest level) national conservation bird species in China in 2021. Birdsong in the breeding season is the main communicative signal under sexual selection, and song variations have long been considered critical evidence of divergence among subspecies or populations. We compared the songs of 89 males from 18 populations to test subspecies taxonomy. We found that songs of the Yellow-breasted Bunting Emberiza aureola are subspecies specific and that three subspecies can be clearly discriminated by song divergences. Moreover, an analysis of multiple vocal traits supports the claim that insulana is distinct from aureola and ornata. Finally, at the geographic population level, populations can be clearly classified in accordance with the three subspecies, although the aureola population in Xinjiang, China is differentiated from other populations of the same subspecies. The results of this study demonstrate that all populations and subspecies are unique and should be protected to maintain intraspecies song diversity. In addition, several specific populations, such as insulana populations in Japan and the Xinjiang, China population of aureola, need to be paid special attention to prevent the extinction of unique or local taxa.Entities:
Keywords: Yellow-breasted Bunting; bird song; insulana; population divergence; subspecies taxonomy
Year: 2022 PMID: 36078012 PMCID: PMC9454650 DOI: 10.3390/ani12172292
Source DB: PubMed Journal: Animals (Basel) ISSN: 2076-2615 Impact factor: 3.231
Figure 1Distribution of Emberiza aureola taxon recordings from nine populations used in the subspecies vocal divergence analysis, with sampling sites indicated by different symbols. Squares represent E. a. aureola (population 1 = Sverdlovsk Oblast, Russia; 2 = Qinghe County, Xinjiang Province, China; 3 = Buryatiya, Russia; 4 = Lake Baikal, Russia), circles represent E. a. ornata (population 5 = northeastern and eastern Mongolia; 6 = Zhalong, Heilongjiang Province, China; 7 = Muraviovka Park, Russian Far East; 8 = Khasyn, Magadanskaya Oblast, Russia), and the triangle represents E. a. insulana (population 9 = Toyotomi, Hokkaido, Japan). Different colors and numbers represent different populations marked in the legend.
Figure 2A typical song of the Yellow-breasted Bunting Emberiza aureola showing an obvious introductory phrase at the beginning, a repeated phrase in which the same syllable appears repeatedly and modulation frequency of adjacent phrases. “a” represents the introductory phrase. “a” “b” “c” and “d” indicate different repeated phrases. The blue arrows indicate three syllables in repeated phrase “a” “d1” and “d2” indicate different elements that are discontinuous tracks in the sonogram of a syllable. “e” “f” and “g” show frequency modulation between neighboring phrases. As for “f” MFpeak is equal to the difference in the peak frequency of “b” and “c”, which is divided by the duration from the start of “b” to the end of “c”; MFrange is equal to the difference in the frequency bandwidth of “b” and “c”, which is divided by the duration from the start of “b” to the end of “c”; and MFmaxmin is equal to the difference in frequency between the end of “b” and the start of “c”, which is divided by the interval between “b” and “c”.
GLM results obtained by extracting principal components for all song parameters of subspecies.
| Variable | Estimate |
|
|
|
|---|---|---|---|---|
| Intercept | 1.944 | 0.059 | 33.049 | 0.000 *** |
| Principal component 1 | 0.018 | 0.059 | 0.311 | 0.757 |
| Principal component 2 | −0.336 | 0.059 | −5.678 | 0.000 *** |
| Principal component 3 | −0.052 | 0.059 | -0.887 | 0.378 |
| Principal component 4 | −0.070 | 0.059 | −1.187 | 0.239 |
| Principal component 5 | −0.006 | 0.059 | −0.094 | 0.925 |
| Principal component 6 | −0.113 | 0.059 | −1.909 | 0.060 |
| Principal component 7 | −0.017 | 0.059 | −0.292 | 0.771 |
*** p < 0.001.
Figure 3Linear discriminant analysis (LDA) indicated that the three subspecies could be separated completely by the first two discriminant functions.
Figure 4The typical song of each subspecies. (A) is from E. a. aureola, (B) is from E. a. ornata and (C) is from E. a. insulana.
GLM results obtained by extracting principal components the all song parameters of populations.
| Variable | Estimate |
|
|
|
|---|---|---|---|---|
| Intercept | 6.088 | 0.225 | 27.028 | 0.000 *** |
| Principal component 1 | −0.186 | 0.227 | −0.823 | 0.413 |
| Principal component 2 | −0.933 | 0.227 | −4.115 | 0.000 *** |
| Principal component 3 | −0.257 | 0.227 | −1.134 | 0.261 |
| Principal component 4 | −0.326 | 0.227 | −1.440 | 0.154 |
| Principal component 5 | 0.103 | 0.227 | 0.456 | 0.650 |
| Principal component 6 | −0.280 | 0.227 | −1.237 | 0.220 |
| Principal component 7 | 0.018 | 0.227 | 0.078 | 0.938 |
*** p < 0.001.
Figure 5LDA indicated that the nine populations could be separated completely by the first two discriminant functions.