植物生态学报 ›› 2025, Vol. 49 ›› Issue (1): 74-82.DOI: 10.17521/cjpe.2024.0095 cstr: 32100.14.cjpe.2024.0095
所属专题: 退化草地恢复理论与技术; 草原与草业
张辉, 赵赟鹏, 刘晓琛, 郭增鹏, 胡国瑞, 冯彦皓, 马妙君*(
)(
)
收稿日期:2024-04-02
接受日期:2024-10-24
出版日期:2025-01-20
发布日期:2025-03-08
通讯作者:
* 马妙君: ORCID: 0000-0001-7046-9574 (mjma@lzu.edu.cn)基金资助:
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
Supported by:摘要:
青藏高原东部高寒草甸局部地区因长期过度放牧而发生退化。土壤种子库是退化生态系统恢复的潜在重要资源, 其在高寒草甸退化过程中的动态及其在退化草地恢复中的作用仍有待探究。该研究在青藏高原东部选择了4个不同退化水平的高寒草甸, 构建了一个退化序列。在这一序列上对植物群落和土壤种子库进行调查, 探究了植物群落及种子库组成和特征在退化序列上的变化规律, 并分析了种子库在植物群落更新和退化高寒草甸恢复中的潜在作用。研究发现: (1)植物群落的物种丰富度和相对多度随高寒草甸的退化而显著降低, 而土壤种子库的物种丰富度呈现先升高后降低的变化规律, 种子密度则显著降低; (2)植物群落与土壤种子库物种组成相似性随退化水平增加而逐渐增加, 即种子库在植物群落更新中的潜在作用随退化水平的增加而增加; (3)相比于植物群落, 种子库对退化的响应有明显的滞后性, 可以在一定程度上缓冲退化对地上植物群落的影响。以上结果说明, 高寒草甸植物群落和土壤种子库对退化的响应不一致, 土壤种子库是退化高寒草甸恢复的重要潜在资源。然而, 土壤种子库对退化的恢复潜力是有限的, 在重度退化水平下, 由于种子库资源的过度损耗, 种子库在修复中的作用下降。以上研究结果可为青藏高原退化高寒草甸的保护、恢复和管理提供科学依据。
张辉, 赵赟鹏, 刘晓琛, 郭增鹏, 胡国瑞, 冯彦皓, 马妙君. 高寒草甸退化过程中土壤种子库的变化及其在植物群落更新中的潜在作用. 植物生态学报, 2025, 49(1): 74-82. DOI: 10.17521/cjpe.2024.0095
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. Chinese Journal of Plant Ecology, 2025, 49(1): 74-82. DOI: 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%. |
表1 青藏高原东部高寒草甸4个退化水平下植物群落优势物种、放牧历史和生境描述
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%. |
图1 青藏高原东部高寒草甸植物群落物种丰富度(A)、相对丰度(B), 以及不同生活型(C, 一年生和多年生物种)的物种丰富度在4个退化水平之间的变化(平均值±标准误)。I、II、III和IV代表高寒草甸的4个退化水平(对照、轻度退化、中度退化以及重度退化)。不同字母表示不同退化水平间差异显著(p < 0.05)。
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).
图2 青藏高原东部高寒草甸地上植物群落和土壤种子库的物种组成沿退化梯度的非度量多维尺度分析(NMDS)排序。I、II、III和IV沿颜色由浅到深代表4个退化水平(对照、轻度退化、中度退化以及重度退化)。
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* |
表2 青藏高原东部高寒草甸土壤种子库之间、地上植物群落之间以及植物群落与土壤种子库间的物种组成在4个退化水平之间的差异分析
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* |
图3 青藏高原东部高寒草甸土壤种子库物种丰富度(A)、不同生活型的物种丰富度(B)、种子密度(C)以及不同生活型的种子密度(D)在4个退化水平之间的变化(平均值±标准误)。I、II、III、和IV代表4个退化水平(对照、轻度退化、中度退化以及重度退化)。不同字母表示不同退化水平间的差异显著(p < 0.05)。
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).
图4 青藏高原东部高寒草甸土壤种子库和地上植物群落物种组成间的Bray-Curtis不相似性沿退化梯度上的变化趋势。I、II、III和IV代表4个退化水平(对照、轻度退化、中度退化以及重度退化)。
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).
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