
Biodiv Sci ›› 2025, Vol. 33 ›› Issue (11): 25382. DOI: 10.17520/biods.2025382 cstr: 32101.14.biods.2025382
• CITES 50th Anniversary: Integrating Science, Policy, and International Action • Previous Articles
Wenqi Wang1, Yongchuan Yang1,*(
)(
), Wei Chang1, Siwei Hu1, Wenbo Mu1, Yan Zeng2,3(
)
Received:2025-09-29
Accepted:2025-12-23
Online:2025-11-20
Published:2025-12-26
Contact:
Yongchuan Yang
Supported by:Wenqi Wang, Yongchuan Yang, Wei Chang, Siwei Hu, Wenbo Mu, Yan Zeng. Community structure, growth characteristics, and potential resource assessment of Nardostachys jatamansi in varied habitats[J]. Biodiv Sci, 2025, 33(11): 25382.
| 样地编号 Sample plot number | 经度 Longitude (°E) | 纬度 Latitude (°N) | 海拔 Altitude (m) | 地形 Topography | 土壤湿度 Soil water content (%) | 生境类型 Habitat type |
|---|---|---|---|---|---|---|
| HY-1 | 103.25 | 32.93 | 3,750 | 山坡坡地 Hillside | 32.90 ± 2.34 | 中生 Mesic |
| HY-2 | 102.60 | 33.09 | 3,539 | 山坡坡地 Hillside | 26.93 ± 2.22 | 中生 Mesic |
| HY-3 | 102.61 | 33.00 | 3,487 | 山坡坡地 Hillside | 23.37 ± 3.32 | 中生 Mesic |
| HY-4 | 102.96 | 33.08 | 3,721 | 山坡坡地 Hillside | 35.9 ± 7.04 | 中生 Mesic |
| HY-5 | 102.31 | 32.66 | 3,495 | 山谷洼地 Valley bottom | 39.03 ± 4.52 | 湿润 Humid |
| HY-6 | 102.61 | 32.75 | 3,621 | 山坡坡地 Hillside | 25.23 ± 4.24 | 中生 Mesic |
| HY-7 | 102.64 | 32.68 | 3,814 | 山坡坡地 Hillside | 26.13 ± 3.54 | 中生 Mesic |
| HY-8 | 102.46 | 32.95 | 3,685 | 河漫滩 Floodplain | 50.43 ± 4.33 | 湿润 Humid |
| HY-9 | 102.61 | 32.87 | 3,495 | 山谷洼地 Valley bottom | 46.40 ± 8.19 | 湿润 Humid |
| HY-10 | 102.61 | 33.03 | 3,481 | 河漫滩 Floodplain | 55.63 ± 3.99 | 湿润 Humid |
| HY-11 | 102.23 | 32.39 | 3,637 | 河漫滩 Floodplain | 48.03 ± 8.02 | 湿润 Humid |
| HY-12 | 102.08 | 32.50 | 3,482 | 河漫滩 Floodplain | 50.46 ± 4.04 | 湿润 Humid |
Table 1 Field survey data sheet for Nardostachys jatamansi in Hongyuan County, Sichuan Province
| 样地编号 Sample plot number | 经度 Longitude (°E) | 纬度 Latitude (°N) | 海拔 Altitude (m) | 地形 Topography | 土壤湿度 Soil water content (%) | 生境类型 Habitat type |
|---|---|---|---|---|---|---|
| HY-1 | 103.25 | 32.93 | 3,750 | 山坡坡地 Hillside | 32.90 ± 2.34 | 中生 Mesic |
| HY-2 | 102.60 | 33.09 | 3,539 | 山坡坡地 Hillside | 26.93 ± 2.22 | 中生 Mesic |
| HY-3 | 102.61 | 33.00 | 3,487 | 山坡坡地 Hillside | 23.37 ± 3.32 | 中生 Mesic |
| HY-4 | 102.96 | 33.08 | 3,721 | 山坡坡地 Hillside | 35.9 ± 7.04 | 中生 Mesic |
| HY-5 | 102.31 | 32.66 | 3,495 | 山谷洼地 Valley bottom | 39.03 ± 4.52 | 湿润 Humid |
| HY-6 | 102.61 | 32.75 | 3,621 | 山坡坡地 Hillside | 25.23 ± 4.24 | 中生 Mesic |
| HY-7 | 102.64 | 32.68 | 3,814 | 山坡坡地 Hillside | 26.13 ± 3.54 | 中生 Mesic |
| HY-8 | 102.46 | 32.95 | 3,685 | 河漫滩 Floodplain | 50.43 ± 4.33 | 湿润 Humid |
| HY-9 | 102.61 | 32.87 | 3,495 | 山谷洼地 Valley bottom | 46.40 ± 8.19 | 湿润 Humid |
| HY-10 | 102.61 | 33.03 | 3,481 | 河漫滩 Floodplain | 55.63 ± 3.99 | 湿润 Humid |
| HY-11 | 102.23 | 32.39 | 3,637 | 河漫滩 Floodplain | 48.03 ± 8.02 | 湿润 Humid |
| HY-12 | 102.08 | 32.50 | 3,482 | 河漫滩 Floodplain | 50.46 ± 4.04 | 湿润 Humid |
Fig. 2 Schematic diagram of transect survey of Nardostachys jatamansi community (a) and its common distribution pattern within a single sample plot (b). Green grids indicate the presence of N. jatamansi, with each grid representing 1% coverage.
| 物种 Species | 频次 Count | 频率 Frequency (%) | 是否药用 Medicinal/Non-medicinal |
|---|---|---|---|
| 甘松 Nardostachys jatamansi | 36 | 3.85 | 是 Medicinal |
| 嵩草 Carex myosuroides | 36 | 3.85 | 否 Non-medicinal |
| 早熟禾 Poa annua | 34 | 3.64 | 是 Medicinal |
| 委陵菜 Potentilla chinensis | 32 | 3.42 | 是 Medicinal |
| 条叶银莲花 Anemone coelestina var. linearis | 30 | 3.21 | 是 Medicinal |
| 喜湿龙胆 Gentiana helophila | 29 | 3.10 | 否 Non-medicinal |
| 老鹳草 Geranium wilfordii | 27 | 2.89 | 是 Medicinal |
| 川西风毛菊 Saussurea dzeurensis | 26 | 2.78 | 是 Medicinal |
| 狼毒 Stellera chamaejasme | 25 | 2.67 | 是 Medicinal |
| 卵萼花锚 Halenia elliptica | 25 | 2.67 | 是 Medicinal |
| 高原唐松草 Thalictrum cultratum | 23 | 2.46 | 是 Medicinal |
| 矮金莲花 Trollius farreri | 22 | 2.35 | 是 Medicinal |
| 珠芽蓼 Bistorta vivipara | 22 | 2.35 | 是 Medicinal |
| 草玉梅 Anemone rivularis | 19 | 2.03 | 是 Medicinal |
| 高原毛茛 Ranunculus tanguticus | 19 | 2.03 | 是 Medicinal |
| 深红龙胆 Gentiana rubicunda | 18 | 1.93 | 是 Medicinal |
| 火绒草 Leontopodium leontopodioides | 17 | 1.82 | 是 Medicinal |
| 米口袋 Gueldenstaedtia verna | 16 | 1.71 | 是 Medicinal |
| 羊茅 Festuca ovina | 16 | 1.71 | 否 Non-medicinal |
| 虉草 Phalaris arundinacea | 16 | 1.71 | 是 Medicinal |
Table 2 Top 20 most frequently encountered species in natural Nardostachys jatamansi communities
| 物种 Species | 频次 Count | 频率 Frequency (%) | 是否药用 Medicinal/Non-medicinal |
|---|---|---|---|
| 甘松 Nardostachys jatamansi | 36 | 3.85 | 是 Medicinal |
| 嵩草 Carex myosuroides | 36 | 3.85 | 否 Non-medicinal |
| 早熟禾 Poa annua | 34 | 3.64 | 是 Medicinal |
| 委陵菜 Potentilla chinensis | 32 | 3.42 | 是 Medicinal |
| 条叶银莲花 Anemone coelestina var. linearis | 30 | 3.21 | 是 Medicinal |
| 喜湿龙胆 Gentiana helophila | 29 | 3.10 | 否 Non-medicinal |
| 老鹳草 Geranium wilfordii | 27 | 2.89 | 是 Medicinal |
| 川西风毛菊 Saussurea dzeurensis | 26 | 2.78 | 是 Medicinal |
| 狼毒 Stellera chamaejasme | 25 | 2.67 | 是 Medicinal |
| 卵萼花锚 Halenia elliptica | 25 | 2.67 | 是 Medicinal |
| 高原唐松草 Thalictrum cultratum | 23 | 2.46 | 是 Medicinal |
| 矮金莲花 Trollius farreri | 22 | 2.35 | 是 Medicinal |
| 珠芽蓼 Bistorta vivipara | 22 | 2.35 | 是 Medicinal |
| 草玉梅 Anemone rivularis | 19 | 2.03 | 是 Medicinal |
| 高原毛茛 Ranunculus tanguticus | 19 | 2.03 | 是 Medicinal |
| 深红龙胆 Gentiana rubicunda | 18 | 1.93 | 是 Medicinal |
| 火绒草 Leontopodium leontopodioides | 17 | 1.82 | 是 Medicinal |
| 米口袋 Gueldenstaedtia verna | 16 | 1.71 | 是 Medicinal |
| 羊茅 Festuca ovina | 16 | 1.71 | 否 Non-medicinal |
| 虉草 Phalaris arundinacea | 16 | 1.71 | 是 Medicinal |
Fig. 3 Diversity characteristics of Nardostachys jatamansi communities across varied habitats. A P-value of < 0.001 indicates that the difference was statistically significant.
Fig. 4 RDA ranking diagram of species composition in natural Nardostachys jatamansi communities (a) and variation partitioning of environmental factors affecting species composition (b). TP, Total phosphorus; SOM, Soil organic matter; SM, Soil water content; MAP, Mean annual precipitation; bio4, Precipitation of driest month.
Fig. 5 Comparison of biomass (a), root-to-shoot ratio (b), and fresh weight to dry weight ratio (c) of Nardostachys jatamansi in varied habitats. A P-value of < 0.05 indicates that the difference was statistically significant.
Fig. 6 Comparison of root length of Nardostachys jatamansi (a) and nardosinone content (b) in varied habitats. A P-value of < 0.05 indicates that the difference was statistically significant.
Fig. 7 Potential habitat suitability probability map (a) and potential habitat distribution map (b) of the natural Nardostachys jatamansi population in Hongyuan County
| 变量 Independent variable | 估计值 Estimate | 标准误 Std. error | t | P |
|---|---|---|---|---|
| (Intercept) | 1389.38 | 441.78 | 3.145 | <0.001 |
| altitude | -0.20 | 0.12 | -1.691 | 0.094 |
| MAT | 291.93 | 86.42 | 3.378 | <0.001 |
| bio3 | -22.78 | 9.97 | -2.284 | 0.024 |
| bio6 | -306.33 | 67.71 | -4.524 | <0.001 |
| bio7 | -180.91 | 43.40 | -4.168 | <0.001 |
| MAP | 0.83 | 0.47 | 1.761 | 0.081 |
| aspect | -0.16 | 0.05 | -3.293 | <0.001 |
| SM | 365.24 | 263.41 | 1.387 | 0.169 |
Table 3 Multivariate linear regression equation for biomass per unit area of Nardostachys jatamansi in Hongyuan County
| 变量 Independent variable | 估计值 Estimate | 标准误 Std. error | t | P |
|---|---|---|---|---|
| (Intercept) | 1389.38 | 441.78 | 3.145 | <0.001 |
| altitude | -0.20 | 0.12 | -1.691 | 0.094 |
| MAT | 291.93 | 86.42 | 3.378 | <0.001 |
| bio3 | -22.78 | 9.97 | -2.284 | 0.024 |
| bio6 | -306.33 | 67.71 | -4.524 | <0.001 |
| bio7 | -180.91 | 43.40 | -4.168 | <0.001 |
| MAP | 0.83 | 0.47 | 1.761 | 0.081 |
| aspect | -0.16 | 0.05 | -3.293 | <0.001 |
| SM | 365.24 | 263.41 | 1.387 | 0.169 |
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