植物生态学报 ›› 2012, Vol. 36 ›› Issue (8): 831-840.DOI: 10.3724/SP.J.1258.2012.00831
收稿日期:
2012-01-04
接受日期:
2012-05-07
出版日期:
2012-01-04
发布日期:
2012-08-21
通讯作者:
闫兴富
作者简介:
* E-mail: xxffyan@126.com
YAN Xing-Fu*(), ZHOU Li-Biao, ZHANG Kao-Wen, ZHOU Yun-Feng
Received:
2012-01-04
Accepted:
2012-05-07
Online:
2012-01-04
Published:
2012-08-21
Contact:
YAN Xing-Fu
摘要:
在宁夏六盘山区龙潭林区华北落叶松(Larix principis-rupprechtii )人工林的不同样带, 按6个密度梯度(3.24、2.56、1.96、1.44、1.00和0.64株·m-2)移栽萌发生根的辽东栎(Quercus wutaishanica)幼苗, 研究了啮齿动物对幼苗子叶取食的密度效应及其对幼苗存活与生长的影响。结果表明, 辽东栎幼苗的子叶留存率随着幼苗密度的增大而减小。2个高密度处理(3.24和2.56株·m-2)的幼苗子叶留存率分别在移栽6周和5周后稳定在最低水平, 分别为8.64%和7.81%; 而2个较低密度处理(1.44和0.64株·m-2)的幼苗在最后一次观测时子叶留存率仍很高, 分别为44.44%和31.25%, 且二者均显著高于其他密度处理(p < 0.05)。受啮齿动物取食的影响, 在从高到低的不同密度处理下, 幼苗的主根留存率分别为64.16%、80.46%、87.23%、80.25%、69.84%和69.84%; 在1.44株·m-2处理下, 顶芽留存率最高(25.23%), 显著大于3.24株·m-2处理(4.19%) (p < 0.05), 其他密度处理的顶芽留存率均不足20%。子叶被动物取食的幼苗和子叶完整幼苗的最终留存率基本一致, 仅在个别密度处理的某一观测时期差异显著; 顶芽被动物取食的幼苗留存率略低于顶芽完整幼苗的留存率, 但个别密度处理完全相反; 不同类型幼苗的留存率随时间推移而上下波动, 可能与幼苗顶芽被动物取食后萌生形成新芽有关。幼苗的株高、基径、叶片数和单株叶面积均随密度的减小而略有增大, 但除株高外, 其他3个生长参数均在1.44株·m-2处理时最大, 与子叶是否被动物取食有一定的对应关系, 即高密度下更多的幼苗丢失了供应其生长所需营养物质的子叶, 从而影响了幼苗的早期生长。研究结果不仅丰富了“负密度效应”理论和种群更新的“增补限制”理论, 也可为六盘山区退化辽东栎灌丛和辽东栎次生林的恢复及生态系统管理提供 参考。
闫兴富, 周立彪, 张靠稳, 周云锋. 不同密度下辽东栎幼苗子叶丢失及其对幼苗存活和生长的影响. 植物生态学报, 2012, 36(8): 831-840. DOI: 10.3724/SP.J.1258.2012.00831
YAN Xing-Fu, ZHOU Li-Biao, ZHANG Kao-Wen, ZHOU Yun-Feng. Cotyledon loss and its effects on survival and growth of Quercus wutaishanica seedlings under different densities. Chinese Journal of Plant Ecology, 2012, 36(8): 831-840. DOI: 10.3724/SP.J.1258.2012.00831
图1 六盘山区华北落叶松人工林内不同密度的辽东栎幼苗的子叶留存率及其动态(平均值±标准偏差)。
Fig. 1 Retention rate of cotyledon and its dynamics of Quercus wutaishanica seedlings with different densities in a Larix principis-rupprechtii plantation of Liupan Mountains (mean ± SD).
图2 六盘山区华北落叶松人工林内不同密度的辽东栎幼苗子叶被啮齿动物取食后主根和顶芽的留存率(平均值±标准偏差)。同一数据系列的相同字母表示差异不显著 (p > 0.05)。
Fig. 2 Retention rate of taproot and apical bud of Quercus wutaishanica seedlings with different densities after cotyledon predation by rodents in a Larix principis-rupprechtii plantation of Liupan Mountains (mean ± SD). Same letters within the same data series indicate no significant difference at 0.05 level.
密度 Density (ind.·m-2) | 子叶被取食幼苗 Cotyledon-predated seedling | 子叶完整幼苗 Cotyledon-intact seedling | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
2010 | 2011 | 2010 | 2011 | ||||||||||
July 21 | August 22 | September 27 | July 15 | September 27 | July 21 | August 22 | September 27 | July 15 | September 27 | ||||
3.24 | 13.70 ± 10.05ab | 24.21 ± 14.40ab | 22.33 ± 11.15a | 18.15 ± 6.74a | 6.84 ± 3.89a | 30.00 ± 26.46a | 47.78 ± 42.99ab | 30.00 ± 26.46ab | 3.33 ± 5.77a | 6.67 ± 11.55a | |||
2.56 | 19.61 ± 9.90ab | 32.18 ± 16.03ab | 28.78 ± 15.84ab | 15.52 ± 17.05ab | 12.42 ± 11.93a | 14.44 ± 17.10a | 10.00 ± 17.32a | 16.67 ± 15.28a | 3.33 ± 5.77a | 0.00 ± 0.00 | |||
1.96 | 23.14 ± 8.30ab | 32.10 ± 10.15a | 26.53 ± 11.36ab | 14.99 ± 7.68a | 13.23 ± 5.59a | 10.23 ± 9.30a | 30.68 ± 27.90ab | 33.18 ± 18.67ab | 6.06 ± 10.50a | 14.39 ± 12.92a | |||
1.44 | 28.05 ± 7.69a | 40.66 ± 5.27a | 38.09 ± 8.02a | 15.43 ± 15.55ab | 18.81 ± 8.08a | 23.44 ± 10.14a | 28.74 ± 11.18ab | 24.82 ± 17.37a | 27.83 ± 20.95ab | 12.86 ± 14.50a | |||
1.00 | 28.39 ± 20.56ab | 31.20 ± 13.43a | 29.47 ± 13.96ab | 17.31 ± 12.73ab | 17.16 ± 7.96a | 24.44 ± 21.43a | 57.78 ± 36.72b | 58.89 ± 8.39b | 41.11 ± 8.39b | 23.33 ± 25.17a | |||
0.64 | 8.59 ± 8.35b | 5.56 ± 9.62b | 13.03 ± 15.38b | 2.78 ± 4.81b | 0.00 ± 0.00 | 6.67 ± 11.55a | 33.89 ± 22.99ab | 0.00 ± 0.00 | 0.00 ± 0.00 | 0.00 ± 0.00 |
表1 六盘山区华北落叶松林内不同密度的辽东栎幼苗子叶被啮齿动物取食和子叶完整幼苗的留存率(%)及其动态(平均值±标准偏差)
Table 1 Retention rates and dynamics of cotyledon-predated by rodents and cotyledon-intact seedlings of Quercus wutaishanica with different densities in a Larix principis-rupprechtii plantation of Liupan Mountains (mean ± SD)
密度 Density (ind.·m-2) | 子叶被取食幼苗 Cotyledon-predated seedling | 子叶完整幼苗 Cotyledon-intact seedling | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
2010 | 2011 | 2010 | 2011 | ||||||||||
July 21 | August 22 | September 27 | July 15 | September 27 | July 21 | August 22 | September 27 | July 15 | September 27 | ||||
3.24 | 13.70 ± 10.05ab | 24.21 ± 14.40ab | 22.33 ± 11.15a | 18.15 ± 6.74a | 6.84 ± 3.89a | 30.00 ± 26.46a | 47.78 ± 42.99ab | 30.00 ± 26.46ab | 3.33 ± 5.77a | 6.67 ± 11.55a | |||
2.56 | 19.61 ± 9.90ab | 32.18 ± 16.03ab | 28.78 ± 15.84ab | 15.52 ± 17.05ab | 12.42 ± 11.93a | 14.44 ± 17.10a | 10.00 ± 17.32a | 16.67 ± 15.28a | 3.33 ± 5.77a | 0.00 ± 0.00 | |||
1.96 | 23.14 ± 8.30ab | 32.10 ± 10.15a | 26.53 ± 11.36ab | 14.99 ± 7.68a | 13.23 ± 5.59a | 10.23 ± 9.30a | 30.68 ± 27.90ab | 33.18 ± 18.67ab | 6.06 ± 10.50a | 14.39 ± 12.92a | |||
1.44 | 28.05 ± 7.69a | 40.66 ± 5.27a | 38.09 ± 8.02a | 15.43 ± 15.55ab | 18.81 ± 8.08a | 23.44 ± 10.14a | 28.74 ± 11.18ab | 24.82 ± 17.37a | 27.83 ± 20.95ab | 12.86 ± 14.50a | |||
1.00 | 28.39 ± 20.56ab | 31.20 ± 13.43a | 29.47 ± 13.96ab | 17.31 ± 12.73ab | 17.16 ± 7.96a | 24.44 ± 21.43a | 57.78 ± 36.72b | 58.89 ± 8.39b | 41.11 ± 8.39b | 23.33 ± 25.17a | |||
0.64 | 8.59 ± 8.35b | 5.56 ± 9.62b | 13.03 ± 15.38b | 2.78 ± 4.81b | 0.00 ± 0.00 | 6.67 ± 11.55a | 33.89 ± 22.99ab | 0.00 ± 0.00 | 0.00 ± 0.00 | 0.00 ± 0.00 |
密度 Density (ind.·m-2) | 顶芽被取食幼苗 Apical bud-predated seedling | 顶芽完整幼苗 Apical bud-intact seedling | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
2010 | 2011 | 2010 | 2011 | ||||||||||
July 21 | August 22 | September 27 | July 15 | September 27 | July 21 | August 22 | September 27 | July 15 | September 27 | ||||
3.24 | 14.53 ± 10.91ab | 22.84 ± 11.84a | 22.84 ± 11.84a | 17.71 ± 5.91a | 6.28 ± 2.88a | 20.83 ± 36.08a | 25.00 ± 43.30a | 20.83 ± 36.08a | 12.50 ± 21.65a | 8.33 ± 14.43a | |||
2.56 | 17.93 ± 9.66ab | 28.01 ± 13.04a | 27.20 ± 14.92a | 12.71 ± 13.05ab | 8.10 ± 5.33ab | 38.89 ± 9.62a | 59.26 ± 8.49a | 37.04 ± 33.95a | 22.22 ± 25.46a | 22.22 ± 25.46a | |||
1.96 | 17.82 ± 5.33a | 30.21 ± 10.29a | 23.92 ± 13.08a | 14.55 ± 9.77ab | 12.39 ± 4.68ab | 60.48 ± 10.72a | 62.38 ± 15.67a | 40.95 ± 40.03a | 18.10 ± 20.27a | 18.10 ± 20.27a | |||
1.44 | 24.22 ± 13.71ab | 38.17 ± 13.82a | 33.05 ± 12.13a | 17.24 ± 18.41ab | 22.79 ± 7.71b | 29.17 ± 26.02a | 47.22 ± 29.26a | 50.00 ± 0.00a | 4.17 ± 7.22a | 4.17 ± 7.22a | |||
1.00 | 22.30 ± 15.17ab | 24.44 ± 9.18a | 24.44 ± 9.18a | 14.68 ± 13.06ab | 12.46 ± 5.77ab | 41.67 ± 38.19a | 41.67 ± 38.19a | 37.50 ± 33.07a | 29.17 ± 26.02a | 16.67 ± 28.88a | |||
0.64 | 7.04 ± 6.12b | 7.04 ± 6.12b | 13.70 ± 15.17a | 3.33 ± 5.77b | 0.00 ± 0.00 | 16.67 ± 28.88a | 16.67 ± 28.88a | 0.00 ± 0.00 | 0.00 ± 0.00 | 0.00 ± 0.00 |
表2 六盘山区华北落叶松林内不同密度的辽东栎幼苗中顶芽被啮齿动物取食和顶芽完整幼苗的留存率(%)及其动态(平均值±标准偏差)
Table 2 Retention rates and dynamics of apical bud-predated by rodents and apical bud-remained seedlings of Quercus wutaishanica with different densities in a Larix principis-rupprechtii plantation of Liupan Mountains (mean ± SD)
密度 Density (ind.·m-2) | 顶芽被取食幼苗 Apical bud-predated seedling | 顶芽完整幼苗 Apical bud-intact seedling | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
2010 | 2011 | 2010 | 2011 | ||||||||||
July 21 | August 22 | September 27 | July 15 | September 27 | July 21 | August 22 | September 27 | July 15 | September 27 | ||||
3.24 | 14.53 ± 10.91ab | 22.84 ± 11.84a | 22.84 ± 11.84a | 17.71 ± 5.91a | 6.28 ± 2.88a | 20.83 ± 36.08a | 25.00 ± 43.30a | 20.83 ± 36.08a | 12.50 ± 21.65a | 8.33 ± 14.43a | |||
2.56 | 17.93 ± 9.66ab | 28.01 ± 13.04a | 27.20 ± 14.92a | 12.71 ± 13.05ab | 8.10 ± 5.33ab | 38.89 ± 9.62a | 59.26 ± 8.49a | 37.04 ± 33.95a | 22.22 ± 25.46a | 22.22 ± 25.46a | |||
1.96 | 17.82 ± 5.33a | 30.21 ± 10.29a | 23.92 ± 13.08a | 14.55 ± 9.77ab | 12.39 ± 4.68ab | 60.48 ± 10.72a | 62.38 ± 15.67a | 40.95 ± 40.03a | 18.10 ± 20.27a | 18.10 ± 20.27a | |||
1.44 | 24.22 ± 13.71ab | 38.17 ± 13.82a | 33.05 ± 12.13a | 17.24 ± 18.41ab | 22.79 ± 7.71b | 29.17 ± 26.02a | 47.22 ± 29.26a | 50.00 ± 0.00a | 4.17 ± 7.22a | 4.17 ± 7.22a | |||
1.00 | 22.30 ± 15.17ab | 24.44 ± 9.18a | 24.44 ± 9.18a | 14.68 ± 13.06ab | 12.46 ± 5.77ab | 41.67 ± 38.19a | 41.67 ± 38.19a | 37.50 ± 33.07a | 29.17 ± 26.02a | 16.67 ± 28.88a | |||
0.64 | 7.04 ± 6.12b | 7.04 ± 6.12b | 13.70 ± 15.17a | 3.33 ± 5.77b | 0.00 ± 0.00 | 16.67 ± 28.88a | 16.67 ± 28.88a | 0.00 ± 0.00 | 0.00 ± 0.00 | 0.00 ± 0.00 |
图3 六盘山区华北落叶松人工林内不同密度的辽东栎幼苗的株高、基径、叶片数、主根长、总干质量、根冠比、单株叶面积和比叶面积(平均值±标准偏差)。同一生长参数的不同密度处理间的相同字母表示差异不显著(p > 0.05)。
Fig. 3 Seedling height, basal stem diameter, leaf number, taproot length, total dry mass, root-shoot ratio, leaf area per seedling and specific leaf area of Quercus wutaishanica seedlings with different densities in a Larix principis-rupprechtii plantation of Liupan Mountains (mean ± SD). Same letters among different density treatments within the same growth parameter indicate no significant difference at 0.05 level.
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