生态环境学报 ›› 2026, Vol. 35 ›› Issue (6): 928-938.DOI: 10.16258/j.cnki.1674-5906.2026.06.010
张凯1,2(
), 李茜1,*(
), 李佳君3, 李本措1, 郭小伟1, 樊博1, 李万年1, 马振升1,2
收稿日期:2025-07-08
修回日期:2026-03-12
接受日期:2026-04-23
出版日期:2026-06-18
发布日期:2026-06-08
通讯作者:
* 李茜,E-mail: 作者简介:张凯(2001年生),男,硕士研究生,主要从事高寒草地土壤生态学研究。E-mail: zhangkai@nwipb.cas.cn
基金资助:
ZHANG Kai1,2(
), LI Qian1,*(
), LI Jiajun3, LI Bencuo1, GUO Xiaowei1, FAN Bo1, LI Wannian1, MA Zhensheng1,2
Received:2025-07-08
Revised:2026-03-12
Accepted:2026-04-23
Online:2026-06-18
Published:2026-06-08
摘要:
为探究退化高寒嵩草草地养分失衡过程及其土壤微生物生物量的变化,以放牧高寒嵩草草地不同退化演替阶段(禾草-矮嵩草群落、矮嵩草群落、加厚期小嵩草群落、开裂期小嵩草群落、杂类草-黑土型次生裸地)为研究对象,以空间代替时间,理清高寒嵩草草地退化过程中植物生物量及土壤养分特征,分析不同退化演替阶段土壤微生物量碳氮变化,探讨植物-土壤-微生物量的协同关系及退化高寒草地的养分失衡过程。结果表明,1)土壤微生物量碳和微生物量氮含量均随退化程度的加剧而呈梯次下降,由禾草-矮嵩草群落的1494.94 mg·kg−1和640.74 mg·kg−1向小嵩草群落递减,在杂类草-黑土型次生裸地降至523.50 mg·kg−1和101.48 mg·kg−1。2)随草地退化演替进行,植被盖度、地上总生物量及禾本科、莎草科、豆科植物的地上生物量和凋落物生物量呈下降趋势。土壤全碳、全氮、有机碳、硝态氮、铵态氮、速效磷和含水量由禾草-矮嵩草群落向杂类草-黑土型次生裸地整体呈下降趋势。3)微生物量碳和氮含量与地上生物量、地下生物量及土壤速效磷、铵态氮、全碳、有机碳、硝态氮呈正相关关系(p<0.05),表明演替过程中植物生物量的减少与土壤养分含量的下降,共同抑制了微生物量碳氮的积累。因此,放牧引起的植物群落生物量降低与土壤碳氮养分失衡是导致高寒草地土壤微生物量碳氮降低的重要原因。
中图分类号:
张凯, 李茜, 李佳君, 李本措, 郭小伟, 樊博, 李万年, 马振升. 退化高寒草地养分失衡过程中土壤微生物量的变化[J]. 生态环境学报, 2026, 35(6): 928-938.
ZHANG Kai, LI Qian, LI Jiajun, LI Bencuo, GUO Xiaowei, FAN Bo, LI Wannian, MA Zhensheng. Changes in Soil Microbial Biomass During Nutrient Imbalance Process in Degraded Alpine Grassland[J]. Ecology and Environmental Sciences, 2026, 35(6): 928-938.
| 演替阶段 | 地上总生物量/ (g·m−2) | 地上植被盖度/ % | 地下总生物量/ (g·m−2) |
|---|---|---|---|
| GK | 329.67±45.70a | 100.00±0.00a | 440.45±156.68bc |
| K | 315.44±94.52a | 98.33±2.58a | 356.80±48.89c |
| KT | 234.97±51.57b | 84.17±9.47b | 692.88±50.09a |
| KC | 229.63±26.10b | 70.83±8.61c | 564.51±51.62ab |
| FB | 78.29±10.26c | 30.33±6.95d | 47.87±17.90d |
表1 不同退化演替状态高寒草地植物总生物量和盖度特征
Table 1 Characteristics of total plant biomass and coverage in different degradation succession states of alpine grasslands
| 演替阶段 | 地上总生物量/ (g·m−2) | 地上植被盖度/ % | 地下总生物量/ (g·m−2) |
|---|---|---|---|
| GK | 329.67±45.70a | 100.00±0.00a | 440.45±156.68bc |
| K | 315.44±94.52a | 98.33±2.58a | 356.80±48.89c |
| KT | 234.97±51.57b | 84.17±9.47b | 692.88±50.09a |
| KC | 229.63±26.10b | 70.83±8.61c | 564.51±51.62ab |
| FB | 78.29±10.26c | 30.33±6.95d | 47.87±17.90d |
| 演替阶段 | 禾本科/ (g·m−2) | 莎草科/ (g·m−2) | 豆科/ (g·m−2) | 杂类草/ (g·m−2) | 凋落物/ (g·m−2) |
|---|---|---|---|---|---|
| GK | 137.12± 17.14a | 41.0± 29.05a | 63.49± 36.43a | 88.06± 14.55a | 41.04± 10.16a |
| K | 162.40± 59.94a | 26.61± 12.85ab | 63.55± 29.70a | 62.88± 8.55a | 35.49± 18.33a |
| KT | 126.91± 99.75a | 10.72± 4.35b | 37.90± 34.32a | 59.44± 24.66a | 8.61± 6.66b |
| KC | 95.39± 7.64a | 19.28± 8.10ab | 38.88± 24.73a | 68.32± 15.12a | 7.76± 5.16b |
| FB | 4.16± 2.38b | - | - | 74.13± 11.65a | - |
表2 不同退化演替阶段高寒草地植物功能群地上生物量及凋落物特征
Table 2 Characteristics of aboveground biomass and litter of plant functional groups in different degradation succession states of alpine grasslands
| 演替阶段 | 禾本科/ (g·m−2) | 莎草科/ (g·m−2) | 豆科/ (g·m−2) | 杂类草/ (g·m−2) | 凋落物/ (g·m−2) |
|---|---|---|---|---|---|
| GK | 137.12± 17.14a | 41.0± 29.05a | 63.49± 36.43a | 88.06± 14.55a | 41.04± 10.16a |
| K | 162.40± 59.94a | 26.61± 12.85ab | 63.55± 29.70a | 62.88± 8.55a | 35.49± 18.33a |
| KT | 126.91± 99.75a | 10.72± 4.35b | 37.90± 34.32a | 59.44± 24.66a | 8.61± 6.66b |
| KC | 95.39± 7.64a | 19.28± 8.10ab | 38.88± 24.73a | 68.32± 15.12a | 7.76± 5.16b |
| FB | 4.16± 2.38b | - | - | 74.13± 11.65a | - |
图5 土壤微生物量碳氮与植物生物量、土壤理化性质的Mantel分析和RDA分析 BGB,地下生物量;AGB,地上生物量;SOC,有机碳;SIC,无机碳;NH4+-N,铵态氮;AP,速效磷;NO3?-N,硝态氮;SWC,含水量
Figure 5 Mantel test and RDA analysis of soil microbial biomass carbon and nitrogen, plant biomass, and soil physicochemical properties
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