植物生态学报 ›› 2010, Vol. 34 ›› Issue (10): 1155-1164.DOI: 10.3773/j.issn.1005-264x.2010.10.004 cstr: 32100.14.j.issn.1005-264x.2010.10.004
周双喜1,2, 吴冬秀1,*(
), 张琳1,2, 施慧秋1,2
收稿日期:2010-05-11
接受日期:2010-06-23
出版日期:2010-05-11
发布日期:2010-10-31
作者简介:* E-mail: wudx@ibcas.ac.cn
ZHOU Shuang-Xi1,2, WU Dong-Xiu1,*(
), ZHANG Lin1,2, SHI Hui-Qiu1,2
Received:2010-05-11
Accepted:2010-06-23
Online:2010-05-11
Published:2010-10-31
摘要:
大针茅(Stipa grandis)是内蒙古草原的优势物种, 研究其幼苗在不同降雨格局下的响应特征, 可以为进一步研究降雨格局变化下内蒙古典型草原的响应特征提供科学依据。在中国科学院内蒙古草原生态系统定位研究站, 利用开顶式生长室进行控制试验模拟降雨格局变化, 研究了大针茅幼苗对总降雨量和降雨间隔时间变化的响应。结果表明: 1)总降雨量增加50%使大针茅幼苗生长季末的地上生物量平均增加23% (p < 0.05), 而降雨间隔时间由5天增长为15天使地上生物量平均增加48.8% (p < 0.001)。2)总降雨量对大针茅幼苗的地下生物量没有显著影响; 而在低降雨量条件下, 降雨间隔时间增长使地下生物量增加56.2% (p < 0.001), 在高降雨量条件下作用不显著。3)总降雨量和降雨间隔时间对根冠比的效应都依赖于对方水平的高低, 总降雨量增大只在较长降雨间隔条件下使根冠比发生改变(-28.4%, p < 0.05), 降雨间隔时间增长只在高降雨量条件下使根冠比发生改变(-28.8%, p < 0.05)。4)处理期间, 在处理时间分别为30天和45天时, 大针茅幼苗地上生物量、地下生物量和总生物量的差异都主要取决于总降雨量; 而在处理时间为75天时, 其差异则都主要取决于降雨间隔时间。该研究得到以下主要结论: 1)降雨间隔时间与总降雨量一样, 是影响大针茅幼苗生长的关键因素之一。2)总降雨量对大针茅幼苗生长的效应与降雨间隔时间的长短紧密相关。3)降雨格局对大针茅幼苗生长的影响机制随着幼苗的生长期不同而改变。
周双喜, 吴冬秀, 张琳, 施慧秋. 降雨格局变化对内蒙古典型草原优势种大针茅幼苗的影响. 植物生态学报, 2010, 34(10): 1155-1164. DOI: 10.3773/j.issn.1005-264x.2010.10.004
ZHOU Shuang-Xi, WU Dong-Xiu, ZHANG Lin, SHI Hui-Qiu. Effects of changing precipitation patterns on seedlings of Stipa grandis, a dominant plant of typical grassland of Inner Mongolia, China. Chinese Journal of Plant Ecology, 2010, 34(10): 1155-1164. DOI: 10.3773/j.issn.1005-264x.2010.10.004
| 月 Month | 月平均气温 Monthly mean air temperature (℃) | 月平均地温 Monthly mean ground temperature (℃) | 蒸发量 Evaporation (mm) |
|---|---|---|---|
| 7 | 19.8 | 25.4 | 283.2 |
| 8 | 18.5 | 22.6 | 295.2 |
| 9 | 11.3 | 13.5 | 202.9 |
表1 中国科学院内蒙古草原生态系统定位研究站2009年7-9月的平均气温、平均地温和月蒸发量
Table 1 Monthly mean air and ground temperature, and evaporation of July, August, and September of 2009 at Inner Mongolia Grassland Ecosystem Research Station of Chinese Academy of Sciences
| 月 Month | 月平均气温 Monthly mean air temperature (℃) | 月平均地温 Monthly mean ground temperature (℃) | 蒸发量 Evaporation (mm) |
|---|---|---|---|
| 7 | 19.8 | 25.4 | 283.2 |
| 8 | 18.5 | 22.6 | 295.2 |
| 9 | 11.3 | 13.5 | 202.9 |
图1 不同降雨格局下大针茅幼苗地上生物量(A)、地下生物量(B)和总生物量(C)的变化(平均值±标准误差, n = 5)。 用单因素方差分析(Tukey post hoc)检验不同降雨格局之间的差异; 显著性差异(p < 0.05)用不同字母标记。I1, 降雨间隔时间为5天; I2, 降雨间隔时间为15天; Q1, 总降雨量150 mm; Q2, 总降雨量225 mm。
Fig. 1 Dynamics of aboveground biomass (A), belowground biomass (B), total biomass (C) of Stipa grandis seedlings in different precipitation patterns (mean ± SE, n = 5). Differences between each group were tested using One-way ANOVA with a Tukey post hoc test of significance; significant differences at p < 0.05 are indicated by different letters. I1, precipitation interval of 5 days; I2, precipitation interval of 15 days; Q1, precipitation quantity of 150 mm; Q2, precipitation quantity of 225 mm.
| 变量 Source of variation | 地上生物量Aboveground biomass | 地下生物量 Belowground biomass | 总生物量 Total biomass | 根冠比自然对数 ln (root / shoot ratio) | 根拓展生物量 Root proliferation biomass to unplanted half bucket area |
|---|---|---|---|---|---|
| 9.30 | |||||
| Q | 5.56* | 0.72 | 3.53 | 3.86 | 0.43 |
| I | 20.48*** | 14.70*** | 23.45*** | 3.46 | 6.46* |
| Q × I | 0.13 | 10.60*** | 0.88 | 6.42* | 8.54** |
| 8.30 | |||||
| Q | 10.56** | 11.04** | 12.21** | 0.65 | 2.36 |
| I | 8.52** | 3.54 | 7.61* | 4.16 | 0.06 |
| Q × I | 0.04 | 1.74 | 0.36 | 1.02 | 2.08 |
| 8.15 | |||||
| Q | 4.72* | 5.85* | 5.75* | 3.26 | 3.35 |
| I | 0.49 | 2.02 | 1.19 | 2.66 | 0.95 |
| Q × I | 0.34 | 0.01 | 0.13 | 1.05 | 0.09 |
| 7.31 | |||||
| Q | 0.40 | 0.51 | 0.50 | 0.31 | 0.02 |
| I | 1.40 | 4.18 | 2.88 | 5.85* | 0.01 |
| Q × I | 0.32 | 0.00 | 0.09 | 0.10 | 0.47 |
表2 总降雨量和降雨间隔时间对大针茅幼苗地上生物量、地下生物量、总生物量、根冠比和根拓展生物量影响的双因素方差分析结果(F值)
Table 2 Results (F-values) based on Two-way ANOVA of the effects of total precipitation quantity and precipitation interval on aboveground biomass, belowground biomass, total biomass, root/shoot ratio, and root proliferation biomass to the unplanted half bucket area of Stipa grandis seedlings
| 变量 Source of variation | 地上生物量Aboveground biomass | 地下生物量 Belowground biomass | 总生物量 Total biomass | 根冠比自然对数 ln (root / shoot ratio) | 根拓展生物量 Root proliferation biomass to unplanted half bucket area |
|---|---|---|---|---|---|
| 9.30 | |||||
| Q | 5.56* | 0.72 | 3.53 | 3.86 | 0.43 |
| I | 20.48*** | 14.70*** | 23.45*** | 3.46 | 6.46* |
| Q × I | 0.13 | 10.60*** | 0.88 | 6.42* | 8.54** |
| 8.30 | |||||
| Q | 10.56** | 11.04** | 12.21** | 0.65 | 2.36 |
| I | 8.52** | 3.54 | 7.61* | 4.16 | 0.06 |
| Q × I | 0.04 | 1.74 | 0.36 | 1.02 | 2.08 |
| 8.15 | |||||
| Q | 4.72* | 5.85* | 5.75* | 3.26 | 3.35 |
| I | 0.49 | 2.02 | 1.19 | 2.66 | 0.95 |
| Q × I | 0.34 | 0.01 | 0.13 | 1.05 | 0.09 |
| 7.31 | |||||
| Q | 0.40 | 0.51 | 0.50 | 0.31 | 0.02 |
| I | 1.40 | 4.18 | 2.88 | 5.85* | 0.01 |
| Q × I | 0.32 | 0.00 | 0.09 | 0.10 | 0.47 |
| 变量 Source of variation | 地上生物量Aboveground biomass | 地下生物量 Belowground biomass | 总生物量 Total biomass | 根冠比自然对数 ln (root / shoot ratio) | 根拓展生物量 Root proliferation biomass to the unplanted half bucket area |
|---|---|---|---|---|---|
| Q | 14.92*** | 12.48** | 17.19*** | 0.02 | 0.87 |
| I | 11.50** | 0.77 | 7.74* | 11.33*** | 1.11 |
| Q × I | 0.00 | 4.61* | 0.68 | 0.35 | 3.55 |
| T | 124.10*** | 135.16*** | 150.13*** | 9.54*** | 92.26*** |
| T × Q | 3.83* | 2.81* | 3.30* | 1.55 | 2.09 |
| T × I | 10.08*** | 6.40*** | 9.83*** | 0.94 | 4.81** |
| T × Q × I | 0.20 | 2.04 | 0.32 | 1.51 | 5.34** |
表3 取样时间、总降雨量、降雨间隔时间对大针茅幼苗地上生物量、地下生物量、总生物量、根冠比和根拓展生物量影响的重复测量的方差分析结果(F值):
Table 3 Results (F-values) based on repeated measures ANOVA of the effects of sampling time, total precipitation quantity and precipitation interval on aboveground biomass, belowground biomass, total biomass, root/shoot ratio, and root proliferation biomass to the unplanted half bucket area of Stipa grandis seedlings
| 变量 Source of variation | 地上生物量Aboveground biomass | 地下生物量 Belowground biomass | 总生物量 Total biomass | 根冠比自然对数 ln (root / shoot ratio) | 根拓展生物量 Root proliferation biomass to the unplanted half bucket area |
|---|---|---|---|---|---|
| Q | 14.92*** | 12.48** | 17.19*** | 0.02 | 0.87 |
| I | 11.50** | 0.77 | 7.74* | 11.33*** | 1.11 |
| Q × I | 0.00 | 4.61* | 0.68 | 0.35 | 3.55 |
| T | 124.10*** | 135.16*** | 150.13*** | 9.54*** | 92.26*** |
| T × Q | 3.83* | 2.81* | 3.30* | 1.55 | 2.09 |
| T × I | 10.08*** | 6.40*** | 9.83*** | 0.94 | 4.81** |
| T × Q × I | 0.20 | 2.04 | 0.32 | 1.51 | 5.34** |
图2 不同降雨格局下大针茅幼苗根冠比的变化(平均值±标准误差, n = 5)。 图注同图1。
Fig. 2 Dynamics of root/shoot ratio of Stipa grandis seedlings in different precipitation patterns (mean ± SE, n = 5). Notes see Fig. 1.
图3 不同降雨格局下大针茅幼苗根拓展生物量的变化(平均值±标准误差, n = 5)。 图注同图1。
Fig. 3 Dynamics of root proliferation biomass of Stipa grandis seedlings to the unplanted half bucket area in different precipitation patterns (mean ± SE, n = 5). Notes see Fig. 1.
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