
Biodiv Sci ›› 2026, Vol. 34 ›› Issue (6): 26050. DOI: 10.17520/biods.2026050 cstr: 32101.14.biods.2026050
• Original Papers: Animal Diversity • Previous Articles Next Articles
Meng Zhang1(
), Rongjun Cao2, Gongfang Wang2, Qiongjiu Zou2, Linting Wu2, Weichang Fu1, Youbing Zhou1, Gangzhi Peng2,*(
)
Received:2026-02-12
Accepted:2026-04-21
Online:2026-06-20
Published:2026-07-30
Contact:
*E-mail: 349625645@qq.com
Supported by:Meng Zhang, Rongjun Cao, Gongfang Wang, Qiongjiu Zou, Linting Wu, Weichang Fu, Youbing Zhou, Gangzhi Peng. Impacts of road disturbance on Artiodactyla: A case study from Hubei Dalaoling National Nature Reserve, China[J]. Biodiv Sci, 2026, 34(6): 26050.
| 物种 Species | 独立有效事件总数 Total no. of valid independent events | 拍摄到的位点数 No. of detected sites | 位点比例 Site proportion (%) | 相对多度指数 Relative abundance index (RAI) |
|---|---|---|---|---|
| 野猪 Sus scrofa | 3,201 | 262 | 81.619 | 5.648 |
| 毛冠鹿 Elaphodus cephalophus | 2,140 | 191 | 59.501 | 5.396 |
| 小麂 Muntiacus reevesi | 12,015 | 249 | 77.570 | 22.500 |
| 中华鬣羚 Capricornis milneedwardsii | 1,322 | 194 | 60.436 | 3.129 |
| 中华斑羚 Naemorhedus griseus | 927 | 152 | 47.352 | 2.727 |
| 林麝 Moschus berezovskii | 829 | 161 | 50.155 | 2.379 |
Table 1 Camera trap detection records of six artiodactyl species in Hubei Dalaoling National Nature Reserve (2020.01-2025.07)
| 物种 Species | 独立有效事件总数 Total no. of valid independent events | 拍摄到的位点数 No. of detected sites | 位点比例 Site proportion (%) | 相对多度指数 Relative abundance index (RAI) |
|---|---|---|---|---|
| 野猪 Sus scrofa | 3,201 | 262 | 81.619 | 5.648 |
| 毛冠鹿 Elaphodus cephalophus | 2,140 | 191 | 59.501 | 5.396 |
| 小麂 Muntiacus reevesi | 12,015 | 249 | 77.570 | 22.500 |
| 中华鬣羚 Capricornis milneedwardsii | 1,322 | 194 | 60.436 | 3.129 |
| 中华斑羚 Naemorhedus griseus | 927 | 152 | 47.352 | 2.727 |
| 林麝 Moschus berezovskii | 829 | 161 | 50.155 | 2.379 |
Fig. 2 Changes in the relative abundance index (RAI) of six artiodactyl species with distance from roads in Hubei Dalaoling National Nature Reserve, based on two-breakpoint generalized linear model (GML). The shaded areas represent the 95% confidence intervals, and the red dashed lines indicate the locations of the breakpoints. (a) Capricornis milneedwardsii; (b) Naemorhedus griseus; (c) Moschus berezovskii; (d) Elaphodus cephalophus; (e) Muntiacus reevesi; (f) Sus scrofa.
Fig. 3 Spearman correlation analysis between species traits and road effect zones. Blue circles represent body weight data, and yellow circles represent diurnal-nocturnal index data. The blue line represents the correlation analysis between body weight and the road effect zone, while the yellow line represents the correlation analysis between the diurnal-nocturnal index and the road effect zone. The diurnal-nocturnal index of Capricornis milneedwardsii is represented by a triangle (identical to that of Moschus berezovskii, both being 0.32).
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