干旱区研究 ›› 2024, Vol. 41 ›› Issue (1): 124-134.doi: 10.13866/j.azr.2024.01.12 cstr: 32277.14.j.azr.2024.01.12
李小锋1(),惠婷婷2,3,4,李耀明2,3,4,毛洁菲2,3,4,王光宇2,3,4,范连连2,3()
收稿日期:
2023-07-14
修回日期:
2023-09-29
出版日期:
2024-01-15
发布日期:
2024-01-24
作者简介:
李小锋(1982-),男,高级畜牧师,硕士,研究方向为草业地理信息、草地管理. E-mail: 基金资助:
LI Xiaofeng1(),HUI Tingting2,3,4,LI Yaoming2,3,4,MAO Jiefei2,3,4,WANG Guangyu2,3,4,FAN Lianlian2,3()
Received:
2023-07-14
Revised:
2023-09-29
Published:
2024-01-15
Online:
2024-01-24
摘要:
本研究基于巴里坤县国家级山地草原监测站10 a植物群落观测数据,探究了长期不同放牧管理方式(长期禁牧M0、冬季放牧M1和全年放牧M2)对新疆山地草原植物群落特征值、植物多样性及多样性与地上生物量之间关系的影响。结果表明:M0、M1和M2对优势种沙生针茅重要值无显著影响,M1和M2提高了非优势及草地退化的指示物种芨芨草、醉马草的重要值;随着放牧强度的增加,群落高度、盖度、密度、地上生物量及其响应比显著下降;Shannon-Wiener多样性指数、Simpson优势度指数和Pielou均匀度指数在各放牧处理下均无显著差异,但Margalef丰富度指数随放牧强度显著增加;M0处理地上生物量与Simpson优势度指数、Shannon-Wiener多样性指数和Pielou均匀度指数负相关,M1处理地上生物量与Margalef丰富度指数负相关。随着处理时间的增加,长期禁牧有利于退化草地的恢复,提高了群落特征值,在一定程度上有利于草地生产力的提高和群落稳定性的维持;放牧会影响生态系统中资源的再分配,导致物种多样性的增加,但是全年放牧管理方式下草地则退化加剧。
李小锋, 惠婷婷, 李耀明, 毛洁菲, 王光宇, 范连连. 不同放牧管理方式对新疆山地草原植物群落特征的影响[J]. 干旱区研究, 2024, 41(1): 124-134.
LI Xiaofeng, HUI Tingting, LI Yaoming, MAO Jiefei, WANG Guangyu, FAN Lianlian. Effects of different grazing management strategies on plant diversity in the mountain grassland of Xinjiang, China[J]. Arid Zone Research, 2024, 41(1): 124-134.
表2
样地植被特征"
序号 | 植物名称 | 高度/cm | 盖度/% | 密度/(per·m-2) | 产草量干重/(g·m-2) |
---|---|---|---|---|---|
1 | 沙生针茅(Stipa glareosa) | 5.66 | 41.67 | 56.00 | 13.01 |
2 | 银灰旋花(Convolvulus ammannii) | 3.31 | 8.33 | 10.33 | 4.28 |
3 | 狗娃花(Heteropappus hispidus) | 10.55 | 1.33 | 3.44 | 1.43 |
4 | 多根葱(Allium polyrhizum) | 11.22 | 2.83 | 5.18 | 1.95 |
5 | 芨芨草(Neotrinia splendens) | 72.73 | 2.00 | 0.49 | 2.39 |
6 | 委陵菜(Potentilla chinensis) | 2.58 | 2.33 | 3.53 | 1.76 |
7 | 醉马草(Achnatherum inebrians) | 77.86 | 1.50 | 0.26 | 1.92 |
8 | 其他 | 2.9 | 1.14 | 0.54 | 0.39 |
表3
不同放牧管理方式下主要物种重要值变化"
种名 | 年份 | M0 | M1 | M2 |
---|---|---|---|---|
沙生针茅(Stipa glareosa) | 2013 | 0.512±0.011Aa | 0.493±0.021Aa | 0.477±0.007Aa |
2017 | 0.494±0.006Aa | 0.504±0.014Aa | 0.494±0.008Aa | |
2022 | 0.596±0.054Aa | 0.490±0.006Aa | 0.491±0.015Aa | |
银灰旋花(Convolvulus ammannii) | 2013 | 0.08±0.002Ab | 0.092±0.004ABab | 0.099±0.007Aa |
2017 | 0.103±0.001Aa | 0.089±0.010Ba | 0.110±0.007Aa | |
2022 | 0.123±0.030Aa | 0.113±0.003Aa | 0.078±0.013Aa | |
狗娃花(Heteropappus hispidus) | 2013 | 0.051±0.003Ab | 0.063±0.007Aab | 0.041±0.003Aa |
2017 | 0.049±0.004ABb | 0.063±0.001Ab | 0.040±0.003Aa | |
2022 | 0.035±0.006Ba | 0.047±0.002Ba | 0.045±0.001Aa | |
多根葱(Allium polyrhizum) | 2013 | 0.075±0.007Aa | 0.071±0.006Aa | 0.058±0.006ABa |
2017 | 0.074±0.002Aa | 0.063±0.006Aa | 0.044±0.005Bb | |
2022 | 0.040±0.009Bb | 0.053±0.004Aab | 0.066±0.002Aa | |
芨芨草(Neotrinia splendens) | 2013 | 0.127±0.001Ab | 0.137±0.003Aa | 0.144±0.002Aa |
2017 | 0.124±0.004Ab | 0.133±0.002Aab | 0.136±0.002ABa | |
2022 | 0.094±0.036Aa | 0.137±0.003Aa | 0.136±0.002Ba | |
委陵菜(Potentilla chinensis) | 2013 | 0.031±0.004Aa | 0.024±0.004Aa | 0.032±0.005Aa |
2017 | 0.033±0.004Aa | 0.023±0.002Aa | 0.028±0.002Aa | |
2022 | 0.026±0.002Aa | 0.032±0.005Aa | 0.025±0.006Aa | |
醉马草(Achnatherum inebrians) | 2013 | 0.124±0.002Ab | 0.119±0.006Ab | 0.149±0.003Ba |
2017 | 0.123±0.006Ab | 0.124±0.001Ab | 0.149±0.004Ba | |
2022 | 0.086±0.035Ab | 0.128±0.002Aab | 0.160±0.002Aa |
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