植物生态学报 ›› 2008, Vol. 32 ›› Issue (4): 838-847.DOI: 10.3773/j.issn.1005-264x.2008.04.012
收稿日期:
2007-04-25
接受日期:
2007-10-30
出版日期:
2008-04-25
发布日期:
2008-07-30
通讯作者:
陈亚宁
作者简介:
*E-mail:chenyn@ms.xjb.ac.cn基金资助:
HAO Xing-Ming1,2, LI Wei-Hong1,2, and CHEN Ya-Ning1,2,*()
Received:
2007-04-25
Accepted:
2007-10-30
Online:
2008-04-25
Published:
2008-07-30
Contact:
and CHEN Ya-Ning
摘要:
该文依据塔里木河下游地下水位多年监测资料, 将地下水位按不同埋深划分为0~2、2~4、4~6、6~8、8~10和>10 m 6个梯度, 并设置植被调查样方进行连续监测, 以分析地下水位变化对植物物种多样性与种群生态位的影响。研究结果表明: 在地下水位2~4 m时, 物种多样性最高, 其次为4~6 m, 再次为0~2 m; 当地下水位在6 m以下时, 物种多样性锐减, Hill多样性指数曲线变化趋势趋于平直化。荒漠河岸(林)植被主要植物种群生态位随着地下水位的逐步下降而扩展, 并在地下水位4~6 m处达到最宽; 尔后, 生态位又显著变窄; 地下水位4~6 m时, 种群间生态位重叠最不显著, 物种数较为丰富。因此, 该文分析得出结论: 塔里木河下游植被恢复的地下水位应确保达到6 m以上, 大部分地区地下水位应维持在4~6 m, 而部分河道附近地区地下水位争取达到2~4 m。
郝兴明, 李卫红, 陈亚宁. 新疆塔里木河下游荒漠河岸(林)植被合理生态水位. 植物生态学报, 2008, 32(4): 838-847. DOI: 10.3773/j.issn.1005-264x.2008.04.012
HAO Xing-Ming, LI Wei-Hong, and CHEN Ya-Ning. WATER TABLE AND THE DESERT RIPARIAN FOREST COMMUNITY IN THE LOWER REACHES OF TARIM RIVER, CHINA. Chinese Journal of Plant Ecology, 2008, 32(4): 838-847. DOI: 10.3773/j.issn.1005-264x.2008.04.012
编号 Number | 种名 Species | 编号 Number | 种名 Species |
---|---|---|---|
1 | 多枝柽柳 Tamarix ramosissima | 11 | 猪毛菜 Salsola sp. |
2 | 胀果甘草 Glycyrrhiza inflata | 12 | 白刺 Nitraria sibirica |
3 | 刚毛柽柳 T.hispida | 13 | 刺沙蓬 Salsola ruthenica |
4 | 黑刺 Lycium ruthenicum | 14 | 假苇拂子茅 Calamagrostis pseudophragmites |
5 | 胡杨 Populus euphratica | 15 | 河西苣 Hexinia polydichotoma |
6 | 花花柴 Karelinia caspica | 16 | 蓼子朴 Inula salsoloides |
7 | 铃铛刺 Halimodendron halodendron | 17 | 牛皮消 Cynanchum sibiricum |
8 | 芦苇 Phragmites communis | 18 | 沙枣 Elaeagnus angustifolia |
9 | 大花罗布麻 Apocynum venetum | 19 | 小獐毛 Aeluropus pungens |
10 | 疏叶骆驼刺 Alhagi sparsifolia |
表1 塔里木河下游19种植物名录
Table 1 The list of 19 species in the lower reaches of Tarim River
编号 Number | 种名 Species | 编号 Number | 种名 Species |
---|---|---|---|
1 | 多枝柽柳 Tamarix ramosissima | 11 | 猪毛菜 Salsola sp. |
2 | 胀果甘草 Glycyrrhiza inflata | 12 | 白刺 Nitraria sibirica |
3 | 刚毛柽柳 T.hispida | 13 | 刺沙蓬 Salsola ruthenica |
4 | 黑刺 Lycium ruthenicum | 14 | 假苇拂子茅 Calamagrostis pseudophragmites |
5 | 胡杨 Populus euphratica | 15 | 河西苣 Hexinia polydichotoma |
6 | 花花柴 Karelinia caspica | 16 | 蓼子朴 Inula salsoloides |
7 | 铃铛刺 Halimodendron halodendron | 17 | 牛皮消 Cynanchum sibiricum |
8 | 芦苇 Phragmites communis | 18 | 沙枣 Elaeagnus angustifolia |
9 | 大花罗布麻 Apocynum venetum | 19 | 小獐毛 Aeluropus pungens |
10 | 疏叶骆驼刺 Alhagi sparsifolia |
物种 Species | 编号Number | 地下水位 Groundwater table | |||||
---|---|---|---|---|---|---|---|
0~2 m | 2~4 m | 4~6 m | 6~8 m | 8~10 m | >10 m | ||
生态位宽度 Niche breadth | |||||||
多枝柽柳 Tamarix ramosissima | 1 | 0 | 1.92 | 3.2 | 2.57 | 2.15 | 1.51 |
胀果甘草 Glycyrrhiza inflata | 2 | 0.64 | 2.49 | 2 | 0.69 | ||
刚毛柽柳 T.hispida | 3 | 1.31 | 2.99 | 1.76 | 0 | 0 | |
黑刺 Lycium ruthenicum | 4 | 0 | 2.54 | 1.69 | 0.87 | ||
胡杨 Populus euphratica | 5 | 0 | 2.33 | 2.79 | 1.93 | 1.35 | |
花花柴 Karelinia caspica | 6 | 1.39 | 1.41 | 0.69 | |||
铃铛刺 Halimodendron halodendron | 7 | 1.1 | 2.37 | 0.69 | |||
芦苇 Phragmites communis | 8 | 0.34 | 1.52 | 2.05 | |||
大花罗布麻 Apocynum venetum | 9 | 0 | 1.73 | 2.05 | 0.69 | 0 | |
疏叶骆驼刺 Alhagi sparsifolia | 10 | 0.63 | 1.88 | 2.41 | 1.37 | ||
猪毛菜 Salsolasp. | 11 | 0.66 | 0.68 | 0.69 | |||
白刺 Nitraria sibirica | 12 | 0.67 | 0.68 | ||||
刺沙蓬 Salsola ruthenica | 13 | 0.67 | |||||
拂子茅 Calamagrostis pseudophragmites | 14 | 0 | |||||
河西苣 Hexinia polydichotoma | 15 | 1.41 | 0 | ||||
蓼子朴 Inula salsoloides | 16 | 0.69 | |||||
牛皮消 Cynanchum sibiricum | 17 | 0 | 0 | ||||
沙枣 Elaeagnus angustifolia | 18 | 0.98 | |||||
小獐毛 Aeluropus pungens | 19 | 1.08 |
表2 塔里木河下游不同地下水位梯度下物种生态位宽度
Table 2 The coefficient of niche breadth along different groundwater table in the lower reach of Tarim River
物种 Species | 编号Number | 地下水位 Groundwater table | |||||
---|---|---|---|---|---|---|---|
0~2 m | 2~4 m | 4~6 m | 6~8 m | 8~10 m | >10 m | ||
生态位宽度 Niche breadth | |||||||
多枝柽柳 Tamarix ramosissima | 1 | 0 | 1.92 | 3.2 | 2.57 | 2.15 | 1.51 |
胀果甘草 Glycyrrhiza inflata | 2 | 0.64 | 2.49 | 2 | 0.69 | ||
刚毛柽柳 T.hispida | 3 | 1.31 | 2.99 | 1.76 | 0 | 0 | |
黑刺 Lycium ruthenicum | 4 | 0 | 2.54 | 1.69 | 0.87 | ||
胡杨 Populus euphratica | 5 | 0 | 2.33 | 2.79 | 1.93 | 1.35 | |
花花柴 Karelinia caspica | 6 | 1.39 | 1.41 | 0.69 | |||
铃铛刺 Halimodendron halodendron | 7 | 1.1 | 2.37 | 0.69 | |||
芦苇 Phragmites communis | 8 | 0.34 | 1.52 | 2.05 | |||
大花罗布麻 Apocynum venetum | 9 | 0 | 1.73 | 2.05 | 0.69 | 0 | |
疏叶骆驼刺 Alhagi sparsifolia | 10 | 0.63 | 1.88 | 2.41 | 1.37 | ||
猪毛菜 Salsolasp. | 11 | 0.66 | 0.68 | 0.69 | |||
白刺 Nitraria sibirica | 12 | 0.67 | 0.68 | ||||
刺沙蓬 Salsola ruthenica | 13 | 0.67 | |||||
拂子茅 Calamagrostis pseudophragmites | 14 | 0 | |||||
河西苣 Hexinia polydichotoma | 15 | 1.41 | 0 | ||||
蓼子朴 Inula salsoloides | 16 | 0.69 | |||||
牛皮消 Cynanchum sibiricum | 17 | 0 | 0 | ||||
沙枣 Elaeagnus angustifolia | 18 | 0.98 | |||||
小獐毛 Aeluropus pungens | 19 | 1.08 |
编号Number | 地下水位 Groundwater table (m) | |||||||||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
0~2 | 2~4 | 4~6 | ||||||||||||||||||||||||||||||||||
2 | 4 | 5 | 8 | 9 | 10 | 2 | 3 | 5 | 6 | 7 | 8 | 9 | 10 | 11 | 2 | 3 | 4 | 5 | 6 | |||||||||||||||||
1 | 0.34 | 0.61 | 0.82 | 0.11 | 0.00 | 0.67 | 0.46 | 0.63 | 0.57 | 0.19 | 0.08 | 0.06 | 0.30 | 0.30 | 0.12 | 0.14 | 0.45 | 0.28 | 0.34 | 0.19 | ||||||||||||||||
2 | 0.73 | 0.52 | 0.77 | 0.66 | 0.67 | 0.31 | 0.70 | 0.16 | 0.33 | 0.35 | 0.19 | 0.35 | 0.05 | 0.27 | 0.13 | 0.12 | 0.00 | |||||||||||||||||||
3 | 0.31 | 0.00 | 0.00 | 0.03 | 0.14 | 0.22 | 0.00 | 0.35 | 0.19 | 0.14 | ||||||||||||||||||||||||||
4 | 0.80 | 0.49 | 0.39 | 0.94 | 0.05 | 0.00 | ||||||||||||||||||||||||||||||
5 | 0.29 | 0.18 | 0.85 | 0.32 | 0.37 | 0.12 | 0.32 | 0.26 | 0.16 | 0.10 | ||||||||||||||||||||||||||
6 | 0.00 | 0.20 | 0.50 | 0.39 | 0.47 | |||||||||||||||||||||||||||||||
7 | 0.00 | 0.00 | 0.00 | 0.00 | ||||||||||||||||||||||||||||||||
8 | 0.89 | 0.44 | 0.36 | 0.46 | 0.02 | |||||||||||||||||||||||||||||||
9 | 0.33 | 0.61 | 0.24 | |||||||||||||||||||||||||||||||||
10 | 0.23 | |||||||||||||||||||||||||||||||||||
编号Number | 地下水位 Groundwater table (m) | |||||||||||||||||||||||||||||||||||
4~6 | 6~8 | 8~10 | >10 | |||||||||||||||||||||||||||||||||
6 | 7 | 8 | 9 | 10 | 11 | 3 | 4 | 5 | 7 | 9 | 11 | 2 | 3 | 4 | 5 | 6 | 9 | 10 | 3 | |||||||||||||||||
1 | 0.19 | 0.30 | 0.19 | 0.19 | 0.30 | 0.06 | 0.31 | 0.42 | 0.30 | 0.04 | 0.17 | 0.10 | 0.20 | 0.07 | 0.33 | 0.39 | 0.20 | 0.13 | 0.44 | 0.05 | ||||||||||||||||
2 | 0.00 | 0.12 | 0.44 | 0.35 | 0.49 | 0.00 | 0.37 | 0.21 | 0.34 | 0.00 | 0.37 | 0.10 | 0.81 | 0.33 | 0.20 | 0.98 | 0.10 | |||||||||||||||||||
3 | 0.14 | 0.28 | 0.15 | 0.38 | 0.32 | 0.00 | 0.12 | 0.12 | 0.10 | 0.06 | 0.06 | 0.33 | 0.10 | 0.00 | 0.10 | |||||||||||||||||||||
4 | 0.00 | 0.68 | 0.24 | 0.25 | 0.29 | 0.00 | 0.15 | 0.20 | 0.10 | 0.10 | ||||||||||||||||||||||||||
5 | 0.10 | 0.06 | 0.14 | 0.07 | 0.15 | 0.09 | 0.21 | 0.00 | 0.00 | 0.20 | 0.10 | 0.20 | ||||||||||||||||||||||||
6 | 0.08 | 0.25 | 0.23 | 0.12 | 0.00 | 0.10 | 0.54 | |||||||||||||||||||||||||||||
7 | 0.14 | 0.33 | 0.27 | 0.00 | 0.00 | 0.00 | ||||||||||||||||||||||||||||||
8 | 0.00 | 0.44 | 0.00 | |||||||||||||||||||||||||||||||||
9 | 0.22 | 0.00 | 0.00 | 0.10 | ||||||||||||||||||||||||||||||||
10 | 0.04 |
表3 塔里木河下游不同地下水位梯度下主要种群生态位重叠
Table 3 The coefficient of niche overlap along different groundwater table in the lower reach of Tarim River
编号Number | 地下水位 Groundwater table (m) | |||||||||||||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
0~2 | 2~4 | 4~6 | ||||||||||||||||||||||||||||||||||
2 | 4 | 5 | 8 | 9 | 10 | 2 | 3 | 5 | 6 | 7 | 8 | 9 | 10 | 11 | 2 | 3 | 4 | 5 | 6 | |||||||||||||||||
1 | 0.34 | 0.61 | 0.82 | 0.11 | 0.00 | 0.67 | 0.46 | 0.63 | 0.57 | 0.19 | 0.08 | 0.06 | 0.30 | 0.30 | 0.12 | 0.14 | 0.45 | 0.28 | 0.34 | 0.19 | ||||||||||||||||
2 | 0.73 | 0.52 | 0.77 | 0.66 | 0.67 | 0.31 | 0.70 | 0.16 | 0.33 | 0.35 | 0.19 | 0.35 | 0.05 | 0.27 | 0.13 | 0.12 | 0.00 | |||||||||||||||||||
3 | 0.31 | 0.00 | 0.00 | 0.03 | 0.14 | 0.22 | 0.00 | 0.35 | 0.19 | 0.14 | ||||||||||||||||||||||||||
4 | 0.80 | 0.49 | 0.39 | 0.94 | 0.05 | 0.00 | ||||||||||||||||||||||||||||||
5 | 0.29 | 0.18 | 0.85 | 0.32 | 0.37 | 0.12 | 0.32 | 0.26 | 0.16 | 0.10 | ||||||||||||||||||||||||||
6 | 0.00 | 0.20 | 0.50 | 0.39 | 0.47 | |||||||||||||||||||||||||||||||
7 | 0.00 | 0.00 | 0.00 | 0.00 | ||||||||||||||||||||||||||||||||
8 | 0.89 | 0.44 | 0.36 | 0.46 | 0.02 | |||||||||||||||||||||||||||||||
9 | 0.33 | 0.61 | 0.24 | |||||||||||||||||||||||||||||||||
10 | 0.23 | |||||||||||||||||||||||||||||||||||
编号Number | 地下水位 Groundwater table (m) | |||||||||||||||||||||||||||||||||||
4~6 | 6~8 | 8~10 | >10 | |||||||||||||||||||||||||||||||||
6 | 7 | 8 | 9 | 10 | 11 | 3 | 4 | 5 | 7 | 9 | 11 | 2 | 3 | 4 | 5 | 6 | 9 | 10 | 3 | |||||||||||||||||
1 | 0.19 | 0.30 | 0.19 | 0.19 | 0.30 | 0.06 | 0.31 | 0.42 | 0.30 | 0.04 | 0.17 | 0.10 | 0.20 | 0.07 | 0.33 | 0.39 | 0.20 | 0.13 | 0.44 | 0.05 | ||||||||||||||||
2 | 0.00 | 0.12 | 0.44 | 0.35 | 0.49 | 0.00 | 0.37 | 0.21 | 0.34 | 0.00 | 0.37 | 0.10 | 0.81 | 0.33 | 0.20 | 0.98 | 0.10 | |||||||||||||||||||
3 | 0.14 | 0.28 | 0.15 | 0.38 | 0.32 | 0.00 | 0.12 | 0.12 | 0.10 | 0.06 | 0.06 | 0.33 | 0.10 | 0.00 | 0.10 | |||||||||||||||||||||
4 | 0.00 | 0.68 | 0.24 | 0.25 | 0.29 | 0.00 | 0.15 | 0.20 | 0.10 | 0.10 | ||||||||||||||||||||||||||
5 | 0.10 | 0.06 | 0.14 | 0.07 | 0.15 | 0.09 | 0.21 | 0.00 | 0.00 | 0.20 | 0.10 | 0.20 | ||||||||||||||||||||||||
6 | 0.08 | 0.25 | 0.23 | 0.12 | 0.00 | 0.10 | 0.54 | |||||||||||||||||||||||||||||
7 | 0.14 | 0.33 | 0.27 | 0.00 | 0.00 | 0.00 | ||||||||||||||||||||||||||||||
8 | 0.00 | 0.44 | 0.00 | |||||||||||||||||||||||||||||||||
9 | 0.22 | 0.00 | 0.00 | 0.10 | ||||||||||||||||||||||||||||||||
10 | 0.04 |
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