Research Article |
Corresponding author: Jiang Zhou ( zhoujiang@ioz.ac.cn ) Academic editor: Melissa TR Hawkins
© 2025 Pengfei Luo, Mingle Mao, Chengrui Yan, Qingqing He, Qin Yang, Huaiqing Deng, Ning Xiao, Jiang Zhou.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Luo P, Mao M, Yan C, He Q, Yang Q, Deng H, Xiao N, Zhou J (2025) A new species of the genus Murina (Chiroptera, Vespertilionidae) from the Southeastern Qinghai-Tibetan Plateau, China. Zoosystematics and Evolution 101(3): 983-997. https://doi.org/10.3897/zse.101.147349
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The tube-nosed bats (genus Murina) are small insectivorous mammals that are primarily distributed in South, East, and Southeast Asia. The Qinghai-Tibet Plateau (QTP) has long been an understudied region in bat surveys, especially for species of small arboreal bats, including Murina. In 2023, we surveyed the southeastern QTP and collected seven individual specimens of Murina. The specimens were identified using combined morphological and molecular data (the mitochondrial Cyt b gene). Phylogenetic analyses identified three unknown clades: Murina sp1, Murina sp2, and Murina sp3. Murina sp1 was most closely related to M. pluvialis, with a genetic distance of 0.09. Murina sp2 was most closely related to M. shuipuensis, with a genetic distance of 0.13, and Murina sp3 was most closely related to M. chrysochaetes, with a genetic distance of 0.15. All three species delimitation methods supported the partitioning of Murina sp1, Murina sp2, and Murina sp3. Herein, we describe a new species, Murina chayuensis sp. nov. (Murina sp1.), that is similar to M. annamitica and M. lorelieae. Owing to the limited number of specimens, Murina sp2 and Murina sp3 are not described in this study. Our results highlight the overlooked diversity of bats in the southeastern QTP, and thus this group warrants further surveys and taxonomic studies.
Cyt b, morphology, taxonomy, tube-nosed bats
The genus Murina Gray, 1842 (Chiroptera: Vespertilionidae) is characterized by tubular nostrils and the back of the interfemoral membrane being covered with hair. The species occur in South, East, and Southeast Asia, including Vietnam, Laos, Malaysia, India, China, and others (
Mountainous regions, although covering only approximately one-eighth of the Earth’s land surface, host nearly one-third of global terrestrial species (
To gain a comprehensive view of the distribution and diversity of bats within the QTP, we surveyed the region, obtaining seven individual specimens of Murina from the southeastern QTP. These specimens represented three distinct taxonomic units and exhibited notable dissimilarities in appearance compared with other species of Murina found in China. Because only one specimen was available for each of Murina sp2 and Murina sp3, in this study, we describe only Murina sp1.
In August 2023, seven specimens were collected in Chayu County (28°29'51.12"N, 97°0'53.87"E, 1511 m above sea level) and Luozha County (28°6'18.73"N, 91°7'22.40"E, 3292 m above sea level) using harp traps (Fig.
Occurrence of Murina species in the southeastern Qinghai-Tibetan Plateau and neighboring areas (the occurrence site data were downloaded from GBIF https://doi.org/10.15468/dl.s3mywg).
To identify the bats, DNA was extracted from a small area of the wing membrane of each bat, followed by polymerase chain reaction (PCR) to amplify a portion of the mitochondrial cytochrome b gene (Cyt b) using the primers Cyt b-F (5′-TAG AAT ATC AGC TTT GGG TG-3′) and Cyt b-R (5′-AAA TCA CCG TTG TAC TTC AAC-3′) (
We collected 40 Cyt b sequences from Murina species and relevant outgroups from NCBI for phylogenetic reconstruction in combination with the obtained sequences (Appendix
Three molecular species delimitation methods were used to aid in species definitions. Assemble species by automatic partitioning (ASAP) enables rapid assessment of species boundaries based on sequence differences (
External and craniodental measurements of the bats were taken using electronic digital calipers to the nearest 0.01 mm according to the method of
A BI tree for Murina was constructed based on the Cyt b gene (1041 bp). The tree mirrored the results from the study of
Bayesian inference (BI) tree and an assessment of Murina species delimitation using ASAP, mPTP, and bPTP based on the mitochondrial Cyt b gene. BI tree node numbers indicate the Bayesian posterior probability (BPP). The black and pink boxes denote the putative species identified by ASAP, mPTP, and bPTP.
The genetic distance between Murina sp1 and M. pluvialis was 0.09, the distance between Murina sp2 and M. shuipuensis was 0.13, and the distance between Murina sp3 and M. chrysochaetes was 0.15 (Table
Genetic distance based on the Kimura 2-parameter model between species calculated from Cyt b sequences.
ID | Species | 1 | 2 | 3 | 4 | 5 | 6 | 7 | 8 | 9 | 10 | 11 | 12 | 13 | 14 | 15 | 16 | 17 | 18 | 19 | 20 | 21 | 22 | 23 | 24 | 25 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
1 | M. annamitica | |||||||||||||||||||||||||
2 | M. aenea | 0.18 | ||||||||||||||||||||||||
3 | M. bicolor | 0.18 | 0.19 | |||||||||||||||||||||||
4 | M. cyclotis | 0.18 | 0.16 | 0.18 | ||||||||||||||||||||||
5 | M. eleryi | 0.18 | 0.17 | 0.20 | 0.18 | |||||||||||||||||||||
6 | M. fanjingshanensis | 0.19 | 0.19 | 0.08 | 0.17 | 0.21 | ||||||||||||||||||||
7 | M. florium | 0.18 | 0.16 | 0.18 | 0.18 | 0.18 | 0.18 | |||||||||||||||||||
8 | M. gracilis | 0.20 | 0.19 | 0.22 | 0.18 | 0.08 | 0.22 | 0.19 | ||||||||||||||||||
9 | M. hilgendorfi | 0.18 | 0.17 | 0.15 | 0.17 | 0.18 | 0.15 | 0.18 | 0.20 | |||||||||||||||||
10 | M. huttonii | 0.20 | 0.19 | 0.19 | 0.17 | 0.19 | 0.20 | 0.20 | 0.18 | 0.20 | ||||||||||||||||
11 | M. jaintiana | 0.17 | 0.18 | 0.17 | 0.15 | 0.19 | 0.16 | 0.15 | 0.19 | 0.18 | 0.20 | |||||||||||||||
12 | M. leucogaster | 0.19 | 0.18 | 0.09 | 0.16 | 0.20 | 0.02 | 0.17 | 0.21 | 0.14 | 0.19 | 0.16 | ||||||||||||||
13 | M. liboensis | 0.18 | 0.18 | 0.20 | 0.08 | 0.20 | 0.19 | 0.18 | 0.20 | 0.19 | 0.19 | 0.17 | 0.18 | |||||||||||||
14 | M. peninsularis | 0.18 | 0.17 | 0.18 | 0.14 | 0.19 | 0.19 | 0.20 | 0.22 | 0.18 | 0.20 | 0.19 | 0.19 | 0.16 | ||||||||||||
15 | M. pluvialis | 0.17 | 0.18 | 0.19 | 0.18 | 0.20 | 0.19 | 0.19 | 0.19 | 0.19 | 0.20 | 0.17 | 0.20 | 0.17 | 0.18 | |||||||||||
16 | M. puta | 0.19 | 0.20 | 0.18 | 0.18 | 0.18 | 0.19 | 0.20 | 0.17 | 0.18 | 0.08 | 0.20 | 0.18 | 0.19 | 0.19 | 0.21 | ||||||||||
17 | M. recondita | 0.19 | 0.18 | 0.21 | 0.19 | 0.08 | 0.21 | 0.19 | 0.05 | 0.19 | 0.18 | 0.19 | 0.21 | 0.21 | 0.22 | 0.19 | 0.18 | |||||||||
18 | M. shuipuensis | 0.15 | 0.19 | 0.12 | 0.16 | 0.20 | 0.11 | 0.17 | 0.20 | 0.14 | 0.18 | 0.16 | 0.12 | 0.18 | 0.18 | 0.17 | 0.16 | 0.19 | ||||||||
19 | M. suilla | 0.19 | 0.14 | 0.21 | 0.17 | 0.19 | 0.19 | 0.08 | 0.20 | 0.18 | 0.20 | 0.17 | 0.19 | 0.17 | 0.19 | 0.18 | 0.21 | 0.19 | 0.17 | |||||||
20 | M. tubinaris | 0.17 | 0.17 | 0.17 | 0.17 | 0.19 | 0.17 | 0.16 | 0.19 | 0.17 | 0.20 | 0.09 | 0.17 | 0.18 | 0.19 | 0.18 | 0.19 | 0.19 | 0.16 | 0.17 | ||||||
21 | M. ussuriensis | 0.17 | 0.17 | 0.18 | 0.17 | 0.19 | 0.19 | 0.20 | 0.20 | 0.16 | 0.17 | 0.19 | 0.20 | 0.18 | 0.18 | 0.18 | 0.17 | 0.19 | 0.18 | 0.19 | 0.20 | |||||
22 | M. chayuensis sp. nov. | 0.17 | 0.18 | 0.18 | 0.17 | 0.20 | 0.18 | 0.17 | 0.19 | 0.19 | 0.19 | 0.17 | 0.18 | 0.17 | 0.17 | 0.09 | 0.19 | 0.20 | 0.17 | 0.18 | 0.17 | 0.17 | ||||
23 | M. sp3. | 0.19 | 0.20 | 0.19 | 0.20 | 0.18 | 0.20 | 0.21 | 0.19 | 0.18 | 0.21 | 0.19 | 0.20 | 0.20 | 0.19 | 0.20 | 0.20 | 0.19 | 0.20 | 0.23 | 0.19 | 0.18 | 0.19 | |||
24 | M. sp2. | 0.20 | 0.19 | 0.15 | 0.16 | 0.20 | 0.13 | 0.18 | 0.22 | 0.15 | 0.20 | 0.19 | 0.13 | 0.19 | 0.17 | 0.20 | 0.18 | 0.22 | 0.13 | 0.19 | 0.18 | 0.20 | 0.19 | 0.20 | ||
25 | M. aff. huttonii | 0.19 | 0.20 | 0.19 | 0.17 | 0.19 | 0.20 | 0.20 | 0.19 | 0.19 | 0.04 | 0.19 | 0.20 | 0.18 | 0.18 | 0.21 | 0.09 | 0.19 | 0.17 | 0.20 | 0.19 | 0.16 | 0.19 | 0.21 | 0.18 | |
26 | M. chrysochaetes | 0.16 | 0.18 | 0.17 | 0.16 | 0.16 | 0.17 | 0.19 | 0.17 | 0.17 | 0.14 | 0.18 | 0.17 | 0.18 | 0.16 | 0.17 | 0.14 | 0.16 | 0.17 | 0.19 | 0.17 | 0.15 | 0.18 | 0.15 | 0.18 | 0.15 |
The ASAP analysis identified 29 species partitions based on the best ASAP scores (Suppl. material
Holotype. • XZ2023107 (36.51 mm FA and 16.83 mm GTL; Figs
We discovered a new species in Chayu County that we named Murina chayuensis sp. nov. We propose the common English name “Chayu Tube-Nosed Bat” and the Chinese name “chá yú guǎn bí fú (察隅管鼻蝠).”
The new species is a medium-sized bat in the genus Murina (FA: 33.49–36.51 mm; Table
Species | Sex | FA | E | GTL | CBL | CCL | ZYW | IOW | BCW |
---|---|---|---|---|---|---|---|---|---|
M. aenea | ♂♂ (n = 3) | 35.00, 35.60 [2] | 14.50, 15.00 [2] | 16.95–17.73 | 15.73–16.19 | 14.97–15.55 | 10.29–10.76 | 4.71–4.87 [2] | 8.15–8.38 |
♀♀ (n = 4) | 34.70–37.40 | 12.70–14.90 | 17.20–17.80 [3] | 15.80–16.39 [3] | 15.00–15.69 [3] | 10.65 [1] | 4.83 [1] | 8.11 | |
M. annamitica | ♂♂ (n = 5) | 30.00–30.90 | 13.10–14.00 [4] | 16.00–16.20 | 14.30–14.80 | \ | 8.70–9.00 | \ | \ |
♀ | 32.2 | 14.5 | 16.4 | 15.1 | \ | 9.4 | \ | \ | |
M. cyclotis | ♂♂ (n = 36) | 29.40–33.00 [35] | 12.00–17.60 [17] | 15.86–17.08 [27] | 14.00–15. 67 [27] | 13.60–15.12 | 8.78–10.05 [35] | 3.92–4.48 | 7.16–8.10 |
♀♀ (n = 40) | 31.60–36.80 | 12.70–16.00 [17] | 16.60–18.18 [25] | 14.95–16.86 [24] | 14.34–16.17 [38] | 9.33–10.43 [37] | 3.99–4.52 [38] | 7.40–8.17 [38] | |
M. fionae | ♂♂ (n = 7) | 34.50–36.30 | 12.10–15.60 [6] | 17.53–19.26 | 15.99–17.49 | 15.32–16.87 | 9.78–10.89 | 4.26–4.85 | 7.75–8.39 |
♀♀ (n = 6) | 35.50–40.10 | 14.90–15.50 [3] | 18.12–19.19 | 16.48–17.45 | 15.82–16.73 | 10.19–10.85 | 4.23–4.75 | 7.84–8.49 | |
M. guilleni | ♂♂ (n = 6) | 31.90–34.00 | 11.40–15.20 | 16.40–17.54 | 14.93–15.83 | 14.47–15.19 | 9.29–9.93 | 4.24–4.44 | 7.65–7.82 |
♀♀ (n = 3) | 35.00–35.90 | 13.50–15.10 | 17.12–18.10 | 15.79–16.43 | 15.09–15.76 | 9.75–10.02 | 4.20–4.44 | 7.53–7.74 | |
M. harrisoni | ♂♂ (n = 5) | 33.40–35.30 | \ | 17.30–17.90 | 15.16–15.80 | \ | 9.74–10.23 | 4.21–4.37 | \ |
♀♀ (n = 5) | 36.80–39.50 | \ | 18.51–18.91 | 16.20–16.65 | \ | 10.68–10.91 | 4.23–4.58 | \ | |
M. huttonii | ♂ | 35.10 | 16.70 | 17.90 | 16.50 | \ | 9.20 | \ | \ |
♀♀ (n = 2) | 35.80, 36.40 | 16.20, 17.40 | 18.10, 18.40 | 16.5, 16.8 | \ | 9.9, 10.02 | \ | \ | |
M. lorelieae | ♂♂ (n = 5) | 29.77–31.35 | 13.74–14.91 | 14.82–15.43 | 14.24–14.28 | \ | 7.86–8.46 | \ | 6.87–7.48 |
♀♀ (n = 8) | 32.41–34.44 | 14.31–15.94 | 15.07–15.94 | 14.28–14.26 | \ | 8.46–9.05 | \ | 7.13–7.69 | |
M. liboensis | ♂♂ (n = 3) | 28.16–30.98 | 11.52–12.92 | 15.54–16.52 | 10.16–11.54 | \ | 7.75–9.32 | \ | 6.32–7.45 |
♀♀ (n = 2) | 32.28, 32.64 | 13.84, 14.37 | 16.30, 16.97 | 13.35, 13.85 | \ | 8.53, 9.32 | \ | 7.67, 7.78 | |
M. peninsularis | ♂♂ (n = 22) | 33.80–38.10 [22] | 11.90–18.80 [13] | 17.39–18.52 | 15.68–16.91 | 14.90–16.41 | 9.76–11.31 | 4.31–4.97 [22] | 7.72–8.48 |
♀♀ (n = 17) | 34.50–39.40 | 13.00–17.00 [12] | 17.59–19.33 | 16.11–17.69 | 15.53–16.89 | 10.12–11.22 | 4.46–4.88 [16] | 7.70–8.58 | |
M. pluvialis | ♂ | 36.60 | \ | 16.40 | \ | 14.50 | 9.26 | 4.32 | \ |
M. rozendaali | ♂♂ (n = 13) | 29.00–31.20 [9] | 12.30–14.10 [7] | 15.47–16.42 [7] | 13.96–14.75 [7] | 13.48–14.10 [7] | 8.73–9.46 [7] | 3.98–4.32 [6] | 7.27–7.50 [7] |
M. tiensa | Unknown (n = 4) | 35.20–40.10 | \ | 17.39–19.43 | \ | \ | \ | \ | \ |
M. chayuensis sp. nov | ♂♂ (n = 4) | 33.49–35.12 | 13.72–14.47 | 15.75–16.35 | 12.91–15.07 | 12.58–14.74 | 8.57–8.94 | 4.45–5.16 | 7.25–7.46 |
♀ | 36.51 | 14.82 | 16.83 | 14.25 | 13.09 | 9.45 | 5.18 | 7.42 | |
Species | Sex | MAW | BCH | CM3L | C1C1W | M3M3W | CM3L | ML | |
M. aenea | ♂♂ (n = 3) | 8.61–8.85 | 6.92–7.48 | 8.15–8.38 | 8.15–8.38 | 6.51–6.62 | 6.51–6.62 | 11.99–12.71 | |
♀♀ (n = 4) | 8.90 | 7.67 | 6.06 | 4.88 | 6.09 | 6.64 | 12.81 | ||
M. annamitica | ♂♂ (n = 5) | 7.50–8.00 | \ | 5.00–5.20 | 3.80–4.10 | \ | 5.00–5.70 | \ | |
♀ | 8.1 | \ | 5.3 | 4.5 | \ | 5.9 | \ | ||
M. cyclotis | ♂♂ (n = 36) | 7. 11–8. 48 | 6.08–7.22 [34] | 5.12–5.68 | 3.73–4.27 | 5.07–5.79 [35] | 5.57–6.18 | 10.52–11.68 [35] | |
♀♀ (n = 40) | 7. 64–8. 58 [38] | 6.10–7.21 [37] | 5.06–6.00 [38] | 4.00–4.68 [37] | 5.18–6.05 [38] | 5.75–6.49 [37] | 11.32–12.78 [37] | ||
M. fionae | ♂♂ (n = 7) | 8.10–8.91 | 6.53–7.50 | 5.72–6.40 | 4.18–4.88 | 5.74–6.25 | 6.30–6.95 | 11.99–13.19 | |
♀♀ (n = 6) | 8.22–8.92 | 6.98–7.48 | 5.78–6.32 | 4.32–4.72 | 5.71–6.24 | 6.33–6.89 | 12.56–13.01 | ||
M. guilleni | ♂♂ (n = 6) | 8.00–8.28 | 6.57–6.91 | 5.44–5.72 | 4.12–4.31 [5] | 5.36–5.80 | 5.83–6.12 | 11.13–11.74 | |
♀♀ (n = 3) | 8.18–8.43 | 6.78–7.10 | 5.50–5.91 | 4.28–4.44 | 5.68–5.87 | 6.01–6.43 | 11.95–12.34 | ||
M. harrisoni | ♂♂ (n = 5) | 8.54–8.93 | \ | 5.63–6.00 | \ | \ | 6.32–6.83 | \ | |
♀♀ (n = 5) | 9.04–9.59 | \ | 6.15–6.39 | \ | \ | 6.24–6.81 | \ | ||
M. huttonii | ♂ | 8.60 | \ | 6.10 | 4.60 | \ | 6.70 | \ | |
♀♀ (n = 2) | 8.50, 8.60 | \ | 6.10, 6.10 | 4.60, 4.70 | \ | 6.70, 6.90 | \ | ||
M. lorelieae | ♂♂ (n = 5) | 6.92–7.47 | \ | 4.70–4.83 | 3.50–3.80 | 5.02–5.48 | 4.73–5.15 | 9.67–9.98 | |
♀♀ (n = 8) | 7.38–7.83 | \ | 4.80–5.00 | 3.71–3.81 | 5.11–5.50 | 4.94–5.09 | 10.32–10.72 | ||
M. liboensis | ♂♂ (n = 3) | 5.02–6.53 | 5.84–7.46 | 4.26–5.13 | 3.04–3.78 | 4.19–5.32 | 4.84–5.53 | 9.67–11.53 | |
♀♀ (n = 2) | 6.73, 7.12 | 7.51, 7.75 | 5.39, 5.58 | 3.99, 4.16 | 5.41, 5.75 | 5.74, 5.94 | 11.63, 12.28 | ||
M. peninsularis | ♂♂ (n = 22) | 8.32–9.39 | 6.79–8.22 | 5.52–6.09 | 4.28–5.28 | 5.45–6.22 | 5.94–8.02 | 11.25–12.92 [21] | |
♀♀ (n = 17) | 8.08–9.62 | 7.10–8.37 | 5.68–6.39 | 4.46–5.26 [16] | 5.69–6.22 [16] | 6.28–6.94 [16] | 12.09–13.59 | ||
M. pluvialis | ♂ | 7.78 | 6.43 | 5.49 | 4.21 | 5.52 | 5.93 | 11.18 | |
M. rozendaali | ♂♂ (n = 13) | 7.34–7.74 [7] | 6.15–6.86 [7] | 5.20–5.50 [7] | 3.77–4.14 [7] | 5.17–5.35 [6] | 5.62–6.02 [6] | 10.55–11.22 [6] | |
M. tiensa | Unknown (n = 4) | \ | \ | 5.82–6.68 | \ | \ | 6.30–7.21 | 11.95–13.62 | |
M. chayuensis sp. nov | ♂♂ (n = 4) | 6.87–7.47 | 6.89–7.60 | 4.83–6.06 | 3.67–3.92 | 5.36–5.72 | 5.23–6.67 | 10.22–11.01 | |
♀ | 7.41 | 6.47 | 5.45 | 4.04 | 5.56 | 5.51 | 11.55 |
In the phylogenetic analyses (Fig.
Murina chayuensis sp. nov. possesses a “cyclotis-type” dentition, characterized by the I3 obscuring the I2, with the basal area of P2 being two-thirds or more than that of P4 (
The skull is medium-sized, with a GTL of 15.75–16.83 mm. The CM3L is 5.14–6.06 mm, which is 0.31–0.37 of the GTL (Table
The mandible is delicate, with 10.22–11.55 mm of ML (Table
Murina chayuensis sp. nov. possesses “cyclotis-type” dentition. Therefore, it is readily distinguished from all species with the “suilla-type” dentition. Within all recognized species that have “cyclotis-type” dentition, M. liboensis and M. rozendaali are much smaller and can be easily distinguished from the new species (FA lower than 33.5 mm; Table
Cranial morphology of other Murina species with the “cyclotis-type” dentition, sourced from Eger & Lim, 2012; Reudi et al. 2012; Soisook, 2013; and
Other Murina species possess “cyclotis-type” dentition that is distributed in the southeastern QTP, including M. huttonii and M. pluvialis. The ear of M. huttonii is longer at 16.20–17.40 mm (vs. 13.72–14.82 mm; Table
M. lorelieae and M. annamitica are similar to Murina chayuensis sp. nov. in fur color and cranial morphology. However, both species have a shorter FA (Table
To date, Murina chayuensis sp. nov. has only been found in Xiachayu Town, Chayu County, Xizang, China. The specimens were captured in harp traps set in mixed coniferous-broad-leaved forest at an altitude of approximately 1500–1600 m. This forest is near Xiachayu Town and local farms, where we also collected six species from five genera: Murina sp2, M. aff. huttonii, Harpiola isodon, Rhinolophus ferrumequinum, Pipistrellus sp., and Myotis sp.
In this study, we described a new bat species, Murina chayuensis sp. nov. (Murina sp1), discovered in Xiachayu Town, Chayu County, Xizang, China. The identification was based on morphological characteristics (see Sec. 3.6) and genetic differences (see Sec. 3.1). The addition of this new species brings the total number of recognized Murina species to 42 (
DNA barcoding, a molecular analysis tool, enables swift species identification (
Based on dental characteristics, Murina bats have traditionally been divided into two species types, “suilla” and “cyclotis” (Corbet & Hill, 1992; Koopman, 1994). Based on the position of I2 and I3 and the crown area of P2 and P4 (Corbet & Hill, 1992), Murina chayuensis sp. nov. belongs to the “cyclotis” type. A cranial morphometric analysis of Murina species by
This study was funded by the Special Foundation for National Science and Technology Basic Research Program of China (2021FY100302), the Survey of Wildlife Resources in Key Areas of Xizang (Phase I) (ZL202203601), and the Survey of Wildlife Resources in Key Areas of Xizang (Phase II) (ZL202303601). We thank LetPub (www.letpub.com.cn) for its linguistic assistance during the preparation of this manuscript.
Species | Locality | Cyt b | Reference |
---|---|---|---|
Harpiocephalus harpia | Taiwan, China | GQ168918 | Han et al. 2009 (unpublished) |
Murina aenea | Malaysia | GQ168906 | Han et al. 2009 (unpublished) |
M. aenea | Malaysia | GQ168907 | Han et al. 2009 (unpublished) |
M. annamitica | Laos | JQ044688 |
|
M. bicolor | Taiwan, China | GQ168919 | Han et al. 2009 (unpublished) |
M. bicolor | Taiwan, China | JQ044696 |
|
M. bicolor | Taiwan, China | GQ168921 | Han et al. 2009 (unpublished) |
Murian chayuensis sp. nov. | Xizang, China | PQ412936 (XZ2024085) | This study |
Murian chayuensis sp. nov. | Xizang, China | PQ412937 (XZ2024086) | This study |
Murian chayuensis sp. nov. | Xizang, China | PQ412938 (XZ2024088) | This study |
Murian chayuensis sp. nov. | Xizang, China | PQ412939 (XZ2024100) | This study |
Murian chayuensis sp. nov. | Xizang, China | PQ412940 (XZ2024107) | This study |
M. chrysochaetes | Xizang, China | PQ422114 (XZ2023084) | This study |
M. cyclotis | Mondolkiri, Cambodia | GQ168916 | Han et al. 2009 (unpublished) |
M. eleryi | Hunan, China | GQ168908 | Han et al. 2009 (unpublished) |
M. fanjingshanensis | Guizhou, China | KT180333 |
|
M. fanjingshanensis | Hunan, China | MF543062 | Huang et al. 2018 |
M. florium | Papua New Guinea | GQ168902 |
|
M. gracilis | Taiwan, China | GQ168900 |
|
M. gracilis | Taiwan, China | KJ198139 |
|
M. gracilis | Taiwan, China | KJ198140 |
|
M. gracilis | Taiwan, China | KJ198141 |
|
M. hilgendorfi | South Korea | GQ168909 | Han et al. 2009 (unpublished) |
M. leucogaster (hilgendorfi) | South Korea | KM893454 | Yoon & Park, 2014 |
M. leucogaster (hilgendorfi) | South Korea | NC025949 | Yoon & Park, 2014 |
M. leucogaster (hilgendorfi) | Japan | AB085733 | Sakai et al. 2003 |
M. leucogaster (hilgendorfi) | China | KX467598 | Luo et al. 2016 (unpublished) |
M. huttonii | China | KU521385 | Zhang et al. 2016 (unpublished) |
M. aff. huttonii | Xizang, China | PQ412943 (XZ2023052) | This study |
M. aff. huttonii | Xizang, China | PQ412944 (XZ2023099) | This study |
M. jaintiana | India | JQ044690 |
|
M. leucogaster | Henan, China | GQ168912 | Han et al. 2009 (unpublished) |
M. leucogaster | China | KF294301 | Wang et al. 2013 (unpublished) |
M. leucogaster | China | KF294302 | Wang et al. 2013 (unpublished) |
M. leucogaster | China | KF294303 | Wang et al. 2013 (unpublished) |
M. leucogaster | China | KF294304 | Wang et al. 2013 (unpublished) |
M. leucogaster | China | JX465367 | Guo et al. 2012 |
M. liboensis | Guizhou, China | MK095626 |
|
M. peninsularis | Mondolkiri, Cambodia | GQ168911 | Han et al. 2009 (unpublished) |
M. pluvialis | India | JQ044689 |
|
M. puta | Taiwan, China | GQ168901 | Han et al. 2009 (unpublished) |
M. recondita | Taiwan, China | KJ198269 |
|
M. recondita | Taiwan, China | KJ198270 |
|
M. shuipuensis | Guizhou, China | MK747249 |
|
M. suilla | Java, Indonesia | GQ168905 | Han et al. 2009 (unpublished) |
M. tubinaris | Mondolkiri, Cambodia | GQ168915 | Han et al. 2009 (unpublished) |
M. ussuriensis | South Korea | JX872285 |
|
M. ussuriensis | South Korea | NC021119 |
|
Murina sp2. | Xizang, China | PQ412942 (XZ2023094) | This study |
Murina sp3. | Xizang, China | PQ412941 (XZ2023048) | This study |
The bat species used in morphological comparisons
Murina harrisoni (
Jiulianshan National Natural Reserve, Jiangxi, China: GZHU15090; GZHU15111; GZHU15124; GZHU15125; GZHU15142; GZHU15157; GZHU15159; GZHU15160; GZHU15161; GZHU15162.
Murina huttonii (Francis & Eger, 2012):
Uttar Pradesh, India: BMNH.79.11.21.685 (holotype); BMNH.14.7.10.32; Darjeeling: BMNH.16.3.25.25.
Murina annamitica (Francis & Eger, 2012):
Nakai Plateau, Khammouan Province, Laos: ROM 106492;
Ban Phoulan, Louangnamtha, Laos: ROM 118394; Nam Et – Phou Louey, Houaphan, Laos: EBD 25753; Tran Don, Quang Nam, Vietnam: ROM 111361;
Binh Phuoc Province, Vietnam: ZMMUS-184673; Annamite Mountains, Bolokhamxai, Laos: ROM 106467 (holotype).
Murina aenea (Soisook, 2013):
Halabala Wildlife Research Station, Wang, Narathiwat, Thailand: PSUZC-MM2012.211, ♀PSUZC-MM2005.6, PSUZC-MM2012.209, PSUZC-MM2012.210; Boripatr Waterfall, Ton Nga Chang WS., Rattaphum, Songkhla, Thailand: PSUZC-MM2005.7; Ulu Chemperoh, Janda Baik, Pahang, Malaysia: BMHN.64.770; Lampunat, Marawi, Kalimantan, Indonesia: MZB30648.
Murina fionae (Soisook, 2013):
Tam Tri, Tam Ky, Quang Nam, C. Vietnam: field number 025; ♂field number 12; ♂field number 18; Phong Nha, C. Vietnam: HZM.8.31764; HZM.6.31759; HZM.7.31762; Huong Hoa Nature Reserve, Quang Tri, C. Vietnam: HNHM.2007.50.3; HNHM.2007.50.4; Pu Mat NP., Nghe An, C. Vietnam: HZM.10.31776; Kon Cha Rang Nature Reserve, Gai Lai, C. Vietnam: HZM.11.32353; Ke Bang, Quang Binh, C. Vietnam: HZM.4.31761; Pu Huong, Nghe An, C. Vietnam: HNHM.2008.23.7; Ngoc Linh Nature Reserve, 10 Km SW Nuoc Xa, Quang Nam, C. Vietnam: ROM MAM 111292; Seima BCA, Mondol Kiri, E. Cambodia: HNHM.2005.81.16.
Murina guilleni (Soisook, 2013):
Rajjaprabha Dam, Ban Takhun, Surat Thani, S. Thailand: PSUZC-MM2010.22 (holotype), PSUZC-MM2010.23 (paratype); Ton Tae Waterfall, Pa Lien, Trang, S. Thailand: PSUZCMM2012.7 (paratype); Khao Nor Chuchi Reserve (=Khao Pra Bang Kram WS.), Krabi, S. Thailand: ROM110439; Wang Tai Nan Waterfall, Manang, Satun, S. Thailand: PSUZCMM 2013.15 (paratype); Ban Ton St., Khao Bantad WS, Phattalung, S. Thailand: PSUZC-MM2012.8; Yaroi Waterfall, Taleban NP., Satun, S. Thailand: PSUZC-MM2008.3; Ban Vang Pha, Songkhla, S. Thailand: PSUZCMM2007.350; Rajjaprabha Dam, Ban Takhun, Surat Thani, S. Thailand: PSUZC-MM2011.42; Makling Waterfall, Rattaphum, Songkhla, S. Thailand: PSUZC-MM2007.154; Great Nicobar Island, Nicobar Islands, India: HZM.14.35312 (holotype of M. sp. nov [A] subsp. nov.); Tillanchong, Nicobar Islands, India: HZM.12.35277 (paratype); Camorta Nicobar Islands, India: HZM.13.35278; Bompuka, Nicobar Islands, India: HNHM.2004.13.1 (paratype); Trinket, Nicobar Islands, India: HZM.15.35319 (paratype).
Murina cyclotis (Soisook, 2013):
Darjeeling, NE. India: BMNH.9.4.4.4 (holotype); Gopaldara, Darjeeling, NE. India: BMNH.16.3.25.28; Pashok, Darjeeling, NE. India: BMNH.16.3.25.29; Teesta Valley, West Bengal, NE. India: BMNH.20.6.24.1; Mousakande, Gammaduwa, Sri Lanka: BMNH.31.9.4.2 (holotype of M. eileenae); Island Jungle Resort, Chitwan NP, Nepal: BMNH.59.5.31.63; BMNH.66.5543; BMNH.72.42.56; ♂HNHM.98.7.3; Madanyan Forest, Manse Township, Kachin, N. Myanmar: HZM.17.35961; Sumka Uma, Kachin, N. Myanmar: BMNH.50.484; Chin Hills, W. Myanmar: BMNH.16.3.26.3; 50 miles from Kindat, Sagaing, W. Myanmar.: BMNH.16.3.26.4; BMNH.16.3.26.89; Hainan Island, China: field number B050023; Hy Nature Reserve, Bac Kan, N. Vietnam: NF.160906.4; NF.170906.5; NF.030706.6; NF.170906.4; NF.230706.4, Kim; Ke Bang, Quang Binh, C. Vietnam: HZM.31760; Pac Ban Village, Tuyen Quang, N. Vietnam: HNHM.98.3.3; Ben En NP., Thanh Hoa, Vietnam: HNHM.2000.84.3; Son La, N. Vietnam: HNHM.2010.42.3; field number T.291107.3; field number T.241107.2; field number T.251107.1; Bai Tu Long NP, Quang Ninh, N. Vietnam: field number T.050808.8; Cat Ba Island, Hai Phong, N. Vietnam: field number T.120806.2; field number T.230408.1; field number T.220908.1; Than Sa, Thai Nguyen, N. Vietnam: field number 11; Pu Hoat NR., Nghe An, C. Vietnam: field number B46; Cuc Phong NP., Ninh Binh, N. Vietnam: HZM.1.30708; HNHM.208.23.1; Pu Mat NP., Nghe An, C. Vietnam: HZM.3.31526; HZM.9.31777; Na Hang NR., Tuyen Quang, N. Vietnam: BMNH.1997.384; Me Linh, Vinh Phuc, N. Vietnam: field number T85; field number T03; field number T.270308.2; Ba Be NP., Bac Kan, N. Vietnam: HNHM.2007.27.7; ♀NTS1597; Tam Dao, Vinh Phuc, N. Vietnam: field number T.010908.10; ♀field number T.010908.6; Phuong Vien, Phu Tho, N. Vietnam: field number T.210708.2; field number T.260607.2; field number T.270607.1; PSUZC-MM.2011.54; Tamtri, Tam Ky, Quang Nam, C. Vietnam: field number T.290708.6, Xuan Son, Phu Tho, N. Vietnam; ♀field number 06; Ban Vieng, Khammouan, C. Laos: BMNH.1999.854; Tham Houay Si, 6.5 km SW. of Ban Vieng, Khammouan, C. Laos: BMNH.1999.51; Vang Vieng, Vientiane, C. Laos: field number BD100320.2; ♀field number BD100320.5; Phou Khao Kouay, Vientiane, C. Laos: ROM MAM 110673; Ban Keng Bit, Nam Kading, Khammouan, C. Laos: SMF85753; Sopkhang, Phongsaly, N. Laos: MHNG.1926.033; Doi Inthanon NP., Chom Thong, Chiang Mai, N. Thailand: BMNH.82.164; Tham Tab Tao, Fang, Chiang Mai, N. Thailand: BMNH.78.2383; Doi Pha Hom Pok, Fang, Chiang Mai, N. Thailand: BMNH.82.165; Chiangdao WS, Chiang Mai, N. Thailand: PSUZCMM2011.32; Klong Lan NP., Kampangphet, NW. Thailand: THNHM-M-821; Phu Suan Sai NP., Na Haew, Loei, NE. Thailand: PSUZC-MM2006.179; PSUZCMM2006.178; Phu Rua, Loei, NE. Thailand: TISTR54-7170; Mo Sing To, Khao Yai NP., 153 Nakhon Ratchasima, NE. Thailand: THNHM-M-735; Dong Sua Parn, Khao Yai NP., Nakhon Ratchasima, NE. Thailand: THNHM-M-775; Klong Klang Khao Ang Ru Nai WS., Chacherngsao, SE. Thailand: PSUZC-MM.2005.203; Phnom Samkos, Pursat, W. Cambodia: HNHM.2007.49.10; Seima BCA, Mondol Kiri, E. Cambodia: HNHM.2006.34.38; HNHM.2005.81.33; HNHM.2005.81.48; Bokor NP., Kampot, SW. Cambodia: HNHM.2006.34.2.
Murina peninsularis (Soisook, 2013):
Khao Pra Bang Kram WS, Klong Tom, Krabi, S. Thailand: PSUZC-MM.2012.9; ♂PSUZC-MM2012.11; ♂PSUZCMM2012.12; ♀PSUZC-MM2012.14; Huay Lek, Khao Nan NP., Nop Pitam, Nakhon Sithammarat, S. Thailand: PSUZC-MM2007.349; Khao Pu Khao Ya NP., Phattalung, S. Thailand: PSUZC-MM 2011.29; Kachong, Khao Bantad WS., Trang, S. Thailand: PSUZC-MM2007.348; Taleban NP., Satun, S. Thailand: PSUZC-MM2006.160; Talow Udang St., Tarutao Island, Satun, S. Thailand: PSUZC-MM2008.137; Pha Dum Waterfall, Ton Nga Chang WS, Songkhla, S. Thailand: PSUZCMM2012.16; PSUZC-MM2012.10; PSUZC-MM2012.12; PSUZC-MM2012.15; Ton Nga Chang WS, Songkhla, S. Thailand: Hala-Bala WS., Wang, Narathiwat, S. Thailand: PSUZC-MM2007.336; PSUZC-MM2011.30; PSUZC-MM2006.120; PSUZCMM2012.155; PSUZC-MM2012.156; PSUZC-MM2012.13; ♂PSUZC-MM2012.196; ♀PSUZC-MM2012.212; ♀PSUZCMM2012.213; Ulu Chemperoh, Janda Baik, Pahang, peninsular Malaysia: BMNH.64.771 (holotype); BMNH.64.772 (paratype); Gunong Benom Base Camp, Bentong, Pahang, peninsular Malaysia: BMNH.73.630; BMNH.67.1607; Taman Negara, Pahang, peninsular Malaysia: TK153526,; Kuala Lompat, Pahang, peninsular Malaysia: CMF920703-03; CMF920705-03; Krau Wildlife Reserve, Pahang, peninsular Malaysia: S401006; Penang, peninsular Malaysia: BMNH.1880.744; Sungai Relembany Camp, Ulu Setiu, Besut, Terengganu, peninsular Malaysia: BMNH.75.1294; Pahang, peninsular Malaysia: BMNH.73.631; Batu Pahat, Kangar, Perlis, peninsular Malaysia: BMNH.68.845;
Fraser Hill, Selangor, peninsular Malaysia: BMNH.64.773; Lojing Highlands, Kelantan, peninsular Malaysia: TK172744; Melinau, Gunung Mulu NP., Sarawak, Borneo: BMNH.78.1543; Sepilok, Sabah, Borneo: BMNH.82.556; BMNH.84.2019; TK168706; Lumerau, Sabah, Borneo: BMNH.84.2020.
Murina lorelieae (Eger & Lim, 2011;
Diding Headwater Forest Nature Preserve, Guangxi Zhuang Autonomous Region, China: ROM MAM 116171 (holotype);
Ailao Nature Reserve, Yunnan Province, China: GZHU14231, GZHU14261, GZHU14268, GZHU14270, GZHU14271, GZHU14275, GZHU14279, GZHU14280, GZHU14281, GZHU14282.
Murina liboensis (
Libo County, Guizhou Province, China: N20160727021 (paratype); N20160727022 (holotype); N20160727023 (paratype); N20160727024 (paratype); N20160727025 (paratype).
Murina rozendaali (Soisook, 2013):
Halabala Wildlife Research Station, Wang, Narathiwat: PSUZC-MM2012.206, PSUZC-MM2012.207, PSUZC-MM2012.208, field number PS130824.3, field number PS130824.4, field number PS130824.6, field number PS130824.7; Gomantong, Sabah, Malaysia: BMNH.83.360 (holotype), BMNH.84.2025; Krau Wildlife Reserve, Malaysia: Pahang BMNH.1999.300, BMNH.1999.301; Park Monggis Substation, Kinabalu NP., Sabah, Malaysia: TTU-M 108241; Suatan, Kaltim, Kalimantan, Indonesia: MZB26735; Way Canguk, Lampung, Sumatra, Indonesia: MZB34991.
Murina tiensa (
Na Ri district of Kim Hy Nature Reserve, Bac Kan Province, Vietnam: HZM.2.38178 (holotype); Bach Thong district of Kim Hy Nature Reserve, Bac Kan Province, Vietnam: HNHM 2007.28.1 (paratype); Na Ri district of Kim Hy Nature Reserve, Bac Kan Province, Vietnam: NF.301006.1 (paratype); Pu Mat National Park, Nghe An Province, Vietnam: HZM 1.31525.
Murina aurata (
Moupin, Sichuan, China: 1870-590 (holotype); 1870-590a (paratype).
Murina pluvialis (
Khasi Hills, Meghalaya, India: MHNG1976.071.
Murina jaintiana (
Jaintia Hills, Meghalaya, India: MHNG1976.072; Chin Hill, Chin State, Myanmar: BM(NH) 16.3.26.5; BM(NH) 16.3.26.7; BM(NH) 16.3.26.8; BM(NH) 16.3.26.85; BM(NH) 16.3.26.86; BM(NH) 16.3.26.87; BM(NH) 16.3.26.88; HNHM2000.20.1.
Murina hkakaboraziensis (
Hkakabo Razi National Park, Putao Township, Kachin, Myanmar: PS160218.6 (holotype).
Murina eleryi (Soisook, 2013):
Doi Inthanon, Chom Thong, Chiang Mai, Thailand: BMNH.82.162 (labeled as M. aurata); Kim Hy Nature Reserve, An Tunh Commune, Na Rai District, Bac Kan Province, Vietnam: HZM.1.39006 (paratype); exact locality not available, Vietnam: field number T120 (ROM field no. 29013); Muong Do Commune, Phu Yen District, Son La Province, Vietnam: field number T.241107.1.
Murina jinchui (
Wolong, Sichuan, China: GZHU 14453 (paratype), GZHU 14454 (paratype), GZHU 14455 (paratype), GZHU 14463 (holotype), GZHU 14461 (paratype), GZHU 14462 (paratype)
A key to the Murina species in the southeastern QTP
1 | Crown area of C1 approximately equal to or less than that of P4; Crown area of P2 approximately half or less than that of P4; I2 situated anterior to I3 | suilla-type 2 |
– | Crown area of C1 approximately equal to or less than that of P4; Crown area of P2 approximately two-thirds or more than that of P4; I2 situated lateral to I3 | cyclotis-type 6 |
2 | Dorsal fur with shiny guard hairs; | 3 |
– | Dorsal fur without shiny guard hairs; | 4 |
3 | P4 exceeds C1 in height | M. aurata |
– | P4 is approximately equal to C1 in height | 5 |
4 | Smaller size, FA less than 31.10 mm; domed braincase; less developed P4 | M. jaintiana |
– | Larger size, FA more than 31.10 mm; braincase flat; more developed P4 | M. jinchui |
5 | Mesostyles of M1 and M2 well developed, with a W-shaped indentation in the labial side; ventral fur whitish gray | M. hkakaboraziensis |
– | Mesostyles of M1 and M2 reduced, with a U-shaped indentation in the labial side; ventral fur creamy white | M. eleryi |
6 | Smaller size, FA less than 33.00 mm in males and 36.80 mm in females | 7 |
– | Larger size, FA more than 33.00 mm in males and 36.80 mm in females | 8 |
7 | Mesostyles of M1 and M2 are well developed, with a W-shaped indentation in the labial side; ventral fur has distinct color bands | M. lorelieae |
– | Mesostyles of M1 and M2 reduced, with a U-shaped indentation in the labial side; ventral fur has indistinct color bands | M. cyclotis |
8 | Talonids of M1 and M2, approximately two-thirds that of trigonids; sagittal crest absent | M. chayuensis sp. nov. |
– | Talonids of M1 and M2, approximately equal to those of trigonids; sagittal crest developed | 9 |
9 | Mesostyles of M1 and M2 well developed, with a W-shaped indentation in the labial side; interfemoral membrane with reddish-brown hairs | M. huttonii |
– | Mesostyles of M1 and M2 reduced, with a U-shaped indentation in the labial side; interfemoral membrane without reddish-brown hairs | M. pluvialis |
Additional information
Data type: docx
Explanation note: fig. S1. Results of the analysis of species definition using ASAP. fig. S2. Results of the analysis of species definition using bPTP. fig. S3. Results of the analysis of species definition using mPTP. table S1. External and cranial measurements (in mm) of each specimen from this study. table S2. External and cranial measurements (in mm) of ‘suilla’ type species distributed in Qinghai-Tibetan Plateau.