Chin J Plant Ecol ›› 2025, Vol. 49 ›› Issue (1): 74-82.DOI: 10.17521/cjpe.2024.0095 cstr: 32100.14.cjpe.2024.0095
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ZHANG Hui, ZHAO Yun-Peng, LIU Xiao-Chen, GUO Zeng-Peng, HU Guo-Rui, FENG Yan-Hao, MA Miao-Jun*()(
)
Received:
2024-04-02
Accepted:
2024-10-24
Online:
2025-01-20
Published:
2025-03-08
Contact:
MA Miao-Jun
Supported by:
ZHANG Hui, ZHAO Yun-Peng, LIU Xiao-Chen, GUO Zeng-Peng, HU Guo-Rui, FENG Yan-Hao, MA Miao-Jun. Dynamics of soil seed bank and its role in plant community regeneration during alpine meadow degradation[J]. Chin J Plant Ecol, 2025, 49(1): 74-82.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2024.0095
退化水平 Degradation level | 优势物种 Dominate species | 生境描述 Habitat description |
---|---|---|
对照 Control (I) | 禾叶嵩草、线叶嵩草、垂穗披碱草、草玉梅 Carex hughii, Carex capillifolia, Elymus nutans, and Anemone rivularis | 生长季适度放牧(5-10月), 放牧家畜为牦牛和藏羊, 该样地是青藏高原东部地区典型的高寒草甸。植物群落的盖度为100%。 Moderate grazing in the growing season (from May to October), the grazing animals are yaks (Bos mutus) and Tibetan sheep (Ovis aries). This sample is a typical alpine meadow in the eastern Qingzang Plateau. The plant community coverage was 100%. |
轻度退化草甸 Light degraded meadow (II) | 禾叶嵩草、垂穗披碱草、草玉梅、鹅绒委陵菜 Carex hughii, Elymus nutans, Anemone rivularis, and Argentina anserina | 生长季放牧强度过高(5-10月), 放牧强度高于对照, 但低于重度退化草甸样地, 放牧的家畜为牦牛和藏羊, 植物群落出现轻度退化, 群落的优势功能群(莎草科和禾本科)的比例减少, 双子叶杂类草数量更多, 局部地区出现小面积斑块。植物群落的盖度为70%-80%。 Overgrazing in the growing season (from May to October). The grazing intensity was higher than that of the control, and the grazing intensity was lower than that of the moderately degraded meadow. The grazing livestock were yaks and Tibetan sheep, the plant community was slightly degraded, the proportion of dominant functional groups (Cyperaceae and Poaceae) of the alpine meadow community decreased, the number of dicotyledonous weeds increased, and a small gap appeared in local areas. The plant community coverage is 70%-80%. |
中度退化草甸 Moderate degraded meadow (III) | 鹅绒委陵菜、草玉梅、密花香薷、细叶亚菊 Argentina anserina, Nemone rivularis, Elsholtzia densa, and Ajania tenuifolia | 生长季过度放牧(5-10月), 放牧强度高于对照和轻度退化草甸, 但低于重度退化草甸样地, 放牧的家畜为牦牛和藏羊, 植物群落出现大面积退化, 群落的优势功能群从莎草科和禾本科转变为双子叶杂类草, 局部地区出现大面积斑块。植物群落的盖度为40%-50%。 Overgrazing in the growing season (from May to October), the grazing intensity was higher than that in the control meadow and light degraded meadows, but lower than that in the seriously degraded meadow plots. The grazing livestock were yaks and Tibetan sheep, and the plant community deteriorated in a large area. The dominant functional group of the community changed from sedge and grass to dicotyledonous weeds, and large gaps appeared in local areas. The plant community coverage is 40%-50%. |
重度退化草甸 Seriously degraded meadow (IV) | 密花香薷、鹅绒委陵菜、草玉梅 Elsholtzia densa, Argentina anserina, and Anemone rivularis | 全面过度放牧(0-12月), 全年长期受到牲畜(如牦牛和藏羊)的过度放牧和践踏, 植物群落物种多样性丧失, 几乎没有禾本科和莎草科植物, 群落被双子叶的杂类草占绝对优势。植物群落的盖度为20%-30%。 Overall overgrazing throughout the year (0-12 months), long-term overgrazing and trampling by livestock (yaks and Tibetan sheep), loss of plant community species diversity, almost no grasses and sedges, the community is dominated by dicotyledonous weeds. The plant community coverage is only 20%-30%. |
Table 1 Description of dominant species of plant communities, grazing history, and habitats under four degradation levels in an alpine meadow on the Qingzang Plateau
退化水平 Degradation level | 优势物种 Dominate species | 生境描述 Habitat description |
---|---|---|
对照 Control (I) | 禾叶嵩草、线叶嵩草、垂穗披碱草、草玉梅 Carex hughii, Carex capillifolia, Elymus nutans, and Anemone rivularis | 生长季适度放牧(5-10月), 放牧家畜为牦牛和藏羊, 该样地是青藏高原东部地区典型的高寒草甸。植物群落的盖度为100%。 Moderate grazing in the growing season (from May to October), the grazing animals are yaks (Bos mutus) and Tibetan sheep (Ovis aries). This sample is a typical alpine meadow in the eastern Qingzang Plateau. The plant community coverage was 100%. |
轻度退化草甸 Light degraded meadow (II) | 禾叶嵩草、垂穗披碱草、草玉梅、鹅绒委陵菜 Carex hughii, Elymus nutans, Anemone rivularis, and Argentina anserina | 生长季放牧强度过高(5-10月), 放牧强度高于对照, 但低于重度退化草甸样地, 放牧的家畜为牦牛和藏羊, 植物群落出现轻度退化, 群落的优势功能群(莎草科和禾本科)的比例减少, 双子叶杂类草数量更多, 局部地区出现小面积斑块。植物群落的盖度为70%-80%。 Overgrazing in the growing season (from May to October). The grazing intensity was higher than that of the control, and the grazing intensity was lower than that of the moderately degraded meadow. The grazing livestock were yaks and Tibetan sheep, the plant community was slightly degraded, the proportion of dominant functional groups (Cyperaceae and Poaceae) of the alpine meadow community decreased, the number of dicotyledonous weeds increased, and a small gap appeared in local areas. The plant community coverage is 70%-80%. |
中度退化草甸 Moderate degraded meadow (III) | 鹅绒委陵菜、草玉梅、密花香薷、细叶亚菊 Argentina anserina, Nemone rivularis, Elsholtzia densa, and Ajania tenuifolia | 生长季过度放牧(5-10月), 放牧强度高于对照和轻度退化草甸, 但低于重度退化草甸样地, 放牧的家畜为牦牛和藏羊, 植物群落出现大面积退化, 群落的优势功能群从莎草科和禾本科转变为双子叶杂类草, 局部地区出现大面积斑块。植物群落的盖度为40%-50%。 Overgrazing in the growing season (from May to October), the grazing intensity was higher than that in the control meadow and light degraded meadows, but lower than that in the seriously degraded meadow plots. The grazing livestock were yaks and Tibetan sheep, and the plant community deteriorated in a large area. The dominant functional group of the community changed from sedge and grass to dicotyledonous weeds, and large gaps appeared in local areas. The plant community coverage is 40%-50%. |
重度退化草甸 Seriously degraded meadow (IV) | 密花香薷、鹅绒委陵菜、草玉梅 Elsholtzia densa, Argentina anserina, and Anemone rivularis | 全面过度放牧(0-12月), 全年长期受到牲畜(如牦牛和藏羊)的过度放牧和践踏, 植物群落物种多样性丧失, 几乎没有禾本科和莎草科植物, 群落被双子叶的杂类草占绝对优势。植物群落的盖度为20%-30%。 Overall overgrazing throughout the year (0-12 months), long-term overgrazing and trampling by livestock (yaks and Tibetan sheep), loss of plant community species diversity, almost no grasses and sedges, the community is dominated by dicotyledonous weeds. The plant community coverage is only 20%-30%. |
Fig. 1 Changes in alpine meadow plant community of species richness (A), relative abundance (B), and species richness of life form (C, annuals and perennials) along four degradation levels (mean ± SE) on the eastern Qingzang Plateau. I to IV represent four degradation levels (control, light degraded meadow, moderate degraded meadow, and seriously degraded meadow). Different letters indicate significant difference between different degradation levels (p < 0.05).
Fig. 2 Non-metric Multidimensional Scaling (NMDS) ordination of species composition of the aboveground vegetation and soil seed bank along a degradation gradient in an alpine meadow on the eastern Qingzang Plateau. I to IV represent four degradation levels (control, light degraded meadow, moderate degraded meadow, and seriously degraded meadow) along the color from light to dark.
群落类型 Community type | 退化水平 Degradation level | R2 | p |
---|---|---|---|
植物群落 Plant community | I vs II | 0.21 | 0.096 |
I vs III | 0.25 | 0.046* | |
I vs IV | 0.57 | 0.015* | |
II vs III | 0.12 | 0.380 | |
II vs IV | 0.42 | 0.015* | |
III vs IV | 0.38 | 0.015* | |
土壤种子库 Soil seed bank | I vs II | 0.55 | 0.015* |
I vs III | 0.62 | 0.015* | |
I vs IV | 0.57 | 0.015* | |
II vs III | 0.18 | 0.096 | |
II vs IV | 0.44 | 0.015* | |
III vs IV | 0.50 | 0.015* | |
植物群落与土壤种子库 Plant community-soil seed bank | I vs I | 0.75 | 0.016* |
II vs II | 0.46 | 0.016* | |
III vs III | 0.44 | 0.015* | |
IV vs IV | 0.49 | 0.015* |
Table 2 Pairwise comparisons of species using PERMANOVA (Permutational multivariate analysis of variance) based on Bray-Curtis dissimilarity among soil seed banks, plant communities, and species composition between aboveground vegetation and seed bank along a degradation gradient in an alpine meadow on the eastern Qingzang Plateau
群落类型 Community type | 退化水平 Degradation level | R2 | p |
---|---|---|---|
植物群落 Plant community | I vs II | 0.21 | 0.096 |
I vs III | 0.25 | 0.046* | |
I vs IV | 0.57 | 0.015* | |
II vs III | 0.12 | 0.380 | |
II vs IV | 0.42 | 0.015* | |
III vs IV | 0.38 | 0.015* | |
土壤种子库 Soil seed bank | I vs II | 0.55 | 0.015* |
I vs III | 0.62 | 0.015* | |
I vs IV | 0.57 | 0.015* | |
II vs III | 0.18 | 0.096 | |
II vs IV | 0.44 | 0.015* | |
III vs IV | 0.50 | 0.015* | |
植物群落与土壤种子库 Plant community-soil seed bank | I vs I | 0.75 | 0.016* |
II vs II | 0.46 | 0.016* | |
III vs III | 0.44 | 0.015* | |
IV vs IV | 0.49 | 0.015* |
Fig. 3 Changes in species richness (A), species richness of different lifeforms (B), seed density (C), and seed density of different lifeforms (D) in alpine meadow seed bank along four degradation levels (mean ± SE) on the eastern Qingzang Plateau. I to IV represent four degradation levels (control, light degraded meadow, moderate degraded meadow, and seriously degraded meadow). Different letters indicate significant differences among the four degradation levels (p < 0.05).
Fig. 4 Bray-Curtis dissimilarity of species composition between seed bank and aboveground vegetation change along a degradation gradient in an alpine meadow on the eastern Qingzang Plateau. I to IV represent four degradation levels (control, light degraded meadow, moderate degraded meadow, and seriously degraded meadow).
[1] | An H, Baskin CC, Ma M (2022). Nonlinear response of the soil seed bank and its role in plant community regeneration with increased grazing disturbance. Journal of Applied Ecology, 59, 2593-2603. |
[2] |
An H, Zhao YP, Ma MJ (2020). Precipitation controls seed bank size and its role in alpine meadow community regeneration with increasing altitude. Global Change Biology, 26, 5767-5777.
DOI PMID |
[3] | Bhattachan A, D’Odorico P, Dintwe K, Okin GS, Collins SL (2014). Resilience and recovery potential of duneland vegetation in the southern Kalahari. Ecosphere, 5, 1-14. DOI: 10.1890/es13-00268.1. |
[4] | Bossuyt B, Honnay O (2008). Can the seed bank be used for ecological restoration? An overview of seed bank characteristics in European communities. Journal of Vegetation Science, 19, 875-884. |
[5] | Brock MA (2011). Persistence of seed banks in Australian temporary wetlands. Freshwater Biology, 56, 1312-1327. |
[6] | Chu H, Zhang C, Dong Q, Shang Z, Degen AA, Yang X, Yu Y, Yang Z, Zhang Y (2019). The effect of grazing intensity and season on the soil seed bank and its relation with above-ground vegetation on the alpine steppe. Agriculture Ecosystems & Environment, 285, 106622. DOI: 10.1016/j.agee.2019.106622. |
[7] | Cooper EJ (2006). Reindeer grazing reduces seed and propagule banks in the high Arctic. Canadian Journal of Botany, 84, 1740-1752. |
[8] | Eskelinen A, Elwood E, Harrison S, Beyen E, Gremer JR (2021). Vulnerability of grassland seed banks to resource-enhancing global changes. Ecology, 102, e03512. DOI: 10.1002/ecy.3512. |
[9] | Eskelinen A, Jessen MT, Bahamonde HA, Bakker JD, Borer ET, Caldeira MC, Harpole WS, Jia M, Lannes LS, Nogueira C, Olde Venterink H, Peri PL, Porath-Krause AJ, Seabloom EW, Schroeder K, et al. (2023). Herbivory and nutrients shape grassland soil seed banks. Nature Communications, 14, 3949. DOI: 10.1038/s41467-023-39677-x. |
[10] | Fenner M, Thompson K (2005). The Ecology of Seeds. Cambridge University Press, Cambridge, UK. |
[11] | Guo Z, Zhao Y, Zhang P, Zhang H, Baskin CC, Zhang T, Chen Y, Hu G, Yang X, Mao H, Zhang Z, Ma M (2024). Rodents mediate the relationship between seed rain, seed bank and plant community with increased grazing disturbance. Ecological Applications, 34, e2984. DOI: 10.1002/eap.2984. |
[12] | He JS, Liu ZP, Yao T, Sun SC, Lü Z, Hu XW, Cao GM, Wu XW, Li L, Bu HY, Zhu JX (2020). Analysis of the main constraints and restoration techniques of degraded grassland on the Tibetan Plateau. Science and Technology Review, 38(17), 66-80. |
[贺金生, 刘志鹏, 姚拓, 孙书存, 吕植, 胡小文, 曹广民, 吴新卫, 李黎, 卜海燕, 朱剑霄 (2020). 青藏高原退化草地恢复的制约因子及修复技术. 科技导报, 38(17), 66-80.]
DOI |
|
[13] | He M, Xin C, Baskin CC, Li J, Zhao Y, An H, Sheng X, Zhao L, Zhao Y, Ma M (2021). Different response of transient and persistent seed bank of alpine wetland to grazing disturbance on the Tibetan Plateau. Plant and Soil, 459, 93-107. |
[14] | Hopfensperger KN (2007). A review of similarity between seed bank and standing vegetation across ecosystems. Oikos, 116, 1438-1448. |
[15] | Kapás RE, Plue J, Kimberley A, Cousins SAO (2020). Grazing livestock increases both vegetation and seed bank diversity in remnant and restored grasslands. Journal of Vegetation Science, 31, 1053-1065. |
[16] | Klaus VH, Schäfer D, Prati D, Busch V, Hamer U, Hoever CJ, Kleinebecker T, Mertens D, Fischer M, Hölzel N (2018). Effects of mowing, grazing and fertilization on soil seed banks in temperate grasslands in Central Europe. Agriculture, Ecosystems & Environment, 256, 211-217. |
[17] | Li J, Okin GS, Alvarez L, Epstein H (2007). Quantitative effects of vegetation cover on wind erosion and soil nutrient loss in a desert grassland of southern New Mexico, USA. Biogeochemistry, 85, 317-332. |
[18] | Liu M, Zhang Z, Sun J, Wang Y, Wang J, Tsunekawa A, Yibeltal M, Xu M, Chen Y (2020). One-year grazing exclusion remarkably restores degraded alpine meadow at Zoige, eastern Tibetan Plateau. Global Ecology and Conservation, 22, e00951. DOI: 10.1016/j.gecco.2020.e00951. |
[19] | Loydi A (2019). Effects of grazing exclusion on vegetation and seed bank composition in a mesic mountain grassland in Argentina. Plant Ecology & Diversity, 12, 127-138. |
[20] | Ma M, Baskin CC, Li WJ, Zhao YP, Zhao Y, Zhao L, Chen N, Du GZ (2019). Seed banks trigger ecological resilience in subalpine meadows abandoned after arable farming on the Tibetan Plateau. Ecological Applications, 29, e01959. DOI: 10.1002/eap.1959. |
[21] | Ma M, Baskin CC, Yu K, Ma Z, Du G (2017). Wetland drying indirectly influences plant community and seed bank diversity through soil pH. Ecological Indicators, 80, 186-195. |
[22] | Ma M, Baskin CC, Zhao YP, An H (2023). Light controls alpine meadow community assembly during succession by affecting species recruitment from the seed bank. Ecological Applications, 33, e2782. DOI: 10.1002/eap.2782. |
[23] | Ma M, Collins SL, Du G (2020). Direct and indirect effects of temperature and precipitation on alpine seed banks in the Tibetan Plateau. Ecological Applications, 30, e02096. DOI: 10.1002/eap.2096. |
[24] | Ma M, Collins SL, Ratajczak Z, Du G (2021). Soil seed banks, alternative stable state theory, and ecosystem resilience. BioScience, 71, 697-707. |
[25] |
Ma M, Walck JL, Ma Z, Wang L, Du G (2018). Grazing disturbance increases transient but decreases persistent soil seed bank. Ecological Applications, 28, 1020-1031.
DOI PMID |
[26] | Ma MJ, Zhou XH, Du GZ (2010a). Role of soil seed bank along a disturbance gradient in an alpine meadow on the Tibet Plateau. Flora, 205, 128-134. |
[27] | Ma MJ, Zhou XH, Wang G, Ma Z, Du GZ (2013). Seasonal dynamics in alpine meadow seed banks along an altitudinal gradient on the Tibetan Plateau. Plant and Soil, 336, 291-302. |
[28] | Ma MJ, Zhou XH, Wang G, Ma Z, Du GZ (2010b). Seasonal dynamics in alpine meadow seed banks along an altitudinal gradient on the Tibetan Plateau. Plant and Soil, 336, 291-302. |
[29] | Matus G, Papp M, Tóthmérész B (2005). Impact of management on vegetation dynamics and seed bank formation of inland dune grassland in Hungary. Flora, 200, 296-306. |
[30] | Noble A, Palmer SM, Glaves DJ, Crowle A, Brown LE, Holden J (2018). Prescribed burning, atmospheric pollution and grazing effects on peatland vegetation composition. Journal of Applied Ecology, 55, 559-569. |
[31] | Plue J, van Calster H, Auestad I, Basto S, Bekker RM, Bruun HH, Chevalier R, Decocq G, Grandin U, Hermy M, Jacquemyn H, Jakobsson A, Jankowska-Błaszczuk M, Kalamees R, Koch MA, et al. (2021). Buffering effects of soil seed banks on plant community composition in response to land use and climate. Global Ecology and Biogeography, 30, 128-139. |
[32] | Sun J, Ma BB, Lu XY (2018). Grazing enhances soil nutrient effects: trade-offs between aboveground and belowground biomass in alpine grasslands of the Tibetan Plateau. Land Degradation & Development, 29, 337-348. |
[33] | Wang X, Ge W, Zhang M, Fernández-Pascual E, Moles A, Saatkamp A, Rosbakh S, Bu H, Panahi P, Ma M (2024). Large and non-spherical seeds are less likely to form a persistent soil seed bank. Proceedings of the Royal Society B: Biological Sciences, 291, 20232764. DOI: 10.1098/rspb.2023.2764. |
[34] |
Zhang C, Willis CG, Burghardt LT, Qi W, Liu K, de Moura Souza-Filho PR, Ma Z, Du G (2014). The community-level effect of light on germination timing in relation to seed mass: a source of regeneration niche differentiation. New Phytologist, 204, 496-506.
DOI PMID |
[35] | Zhao YP, Liao JC, Bao XK, Ma MJ (2021). Soil seed bank dynamics are regulated by bird diversity and soil moisture during alpine wetland degradation. Biological Conservation, 263, 109360. DOI: 10.1016/j.biocon.2021.109360. |
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