生物多样性 ›› 2012, Vol. 20 ›› Issue (4): 427-436. DOI: 10.3724/SP.J.1003.2012.10193
收稿日期:
2011-10-27
接受日期:
2012-03-20
出版日期:
2012-07-20
发布日期:
2012-09-12
通讯作者:
闫兴富
作者简介:
*E-mail: xxffyan@126.com基金资助:
Xingfu Yan1,*(), Yangchun Yu2, Libiao Zhou1, Yunfeng Zhou1
Received:
2011-10-27
Accepted:
2012-03-20
Online:
2012-07-20
Published:
2012-09-12
Contact:
Xingfu Yan
摘要:
为了阐明不同种子投放方式和覆盖处理对啮齿动物取食和搬运/贮藏种子行为的影响, 2010年春季, 我们在宁夏六盘山区的辽东栎幼林, 用塑料标签标记法研究了不同种子投放方式(单独投放、两两组合投放和混合投放)和覆盖处理(对照、凋落物覆盖和土壤覆盖)下啮齿动物对辽东栎、野李和华山松种子的取食和搬运特点。结果表明: (1)不同物种、不同种子投放方式和覆盖处理对种子的就地取食率、搬运后的取食率和贮藏率均具有显著影响, 种子较大或具有厚而坚硬的种皮(内果皮)、组合和混合投放及覆盖处理均不同程度地促进啮齿动物对种子的搬运; (2)3种植物的种子被搬运后取食和贮藏的平均距离范围均在5.5 m以内, 而且种子被搬运后贮藏的距离均大于搬运后取食的距离, 其中华山松种子被搬运后取食的距离显著大于辽东栎和野李种子, 但搬运后的贮藏距离显著小于后两者。(3)种子被搬运后单个种子的取食点和贮藏点占多数, 其他大小的取食点和贮藏点较少, 种子被搬运后以土壤埋藏为主要的贮藏方式。结果表明, 种子的种皮特征以及种子在群落中的分布方式和存在状态, 可能通过延长啮齿动物处理的时间而增大啮齿动物的被捕食风险, 使动物改变对种子的取食和搬运行为, 进而决定了种子的命运。
闫兴富, 余杨春, 周立彪, 周云峰 (2012) 啮齿动物对六盘山区辽东栎、野李和华山松种子的取食和搬运. 生物多样性, 20, 427-436. DOI: 10.3724/SP.J.1003.2012.10193.
Xingfu Yan, Yangchun Yu, Libiao Zhou, Yunfeng Zhou (2012) Seed predation and removal of Quercus wutaishanica, Prunus salicina and Pinus armandii by rodents in the Liupan Mountains. Biodiversity Science, 20, 427-436. DOI: 10.3724/SP.J.1003.2012.10193.
图1 不同覆盖处理的种子投放点在样带上的分布示意图(每一圆圈表示一个种子投放点)。C, 对照; LC, 凋落物覆盖; SC, 土壤覆盖。
Fig. 1 Distribution diagram of releasing plots of different coverage treatments in sample transect. Each circle indicates a releasing plot of seeds. C, Control; LC, Litter coverage; SC, Soil coverage.
变量 Variable | 就地取食 Predation in situ | 搬运后取食 Predation after removal | 搬运后贮藏 Hoarding after removal | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
df | F | P | df | F | P | df | F | P | |||
S | 2 | 37.1 | 0.000 | 2 | 7.1 | 0.001 | 2 | 7.7 | 0.001 | ||
RM | 2 | 8.7 | 0.000 | 2 | 7.7 | 0.001 | 2 | 9 | 0.000 | ||
CT | 2 | 1.3 | 0.281 | 2 | 11.7 | 0.000 | 2 | 3.4 | 0.038 | ||
S×RM | 4 | 8.3 | 0.000 | 4 | 7.1 | 0.000 | 4 | 4.6 | 0.002 | ||
S×CT | 4 | 3.5 | 0.011 | 4 | 4.1 | 0.004 | 4 | 10.8 | 0.000 | ||
RM×CT | 4 | 1.1 | 0.358 | 4 | 2.1 | 0.095 | 4 | 5.6 | 0.001 | ||
S×RM×CT | 8 | 1.5 | 0.177 | 8 | 1.9 | 0.064 | 8 | 1.5 | 0.171 |
表1 不同物种、投放方式和覆盖处理对啮齿动物取食、搬运辽东栎、野李和华山松种子影响的多因素方差分析
Table 1 Multi-way analysis of variance on effects of different species, releasing methods and coverage treatments on seed predation and removal of Quercus wutaishanica, Prunus salicina and Pinus armandii by rodents
变量 Variable | 就地取食 Predation in situ | 搬运后取食 Predation after removal | 搬运后贮藏 Hoarding after removal | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|
df | F | P | df | F | P | df | F | P | |||
S | 2 | 37.1 | 0.000 | 2 | 7.1 | 0.001 | 2 | 7.7 | 0.001 | ||
RM | 2 | 8.7 | 0.000 | 2 | 7.7 | 0.001 | 2 | 9 | 0.000 | ||
CT | 2 | 1.3 | 0.281 | 2 | 11.7 | 0.000 | 2 | 3.4 | 0.038 | ||
S×RM | 4 | 8.3 | 0.000 | 4 | 7.1 | 0.000 | 4 | 4.6 | 0.002 | ||
S×CT | 4 | 3.5 | 0.011 | 4 | 4.1 | 0.004 | 4 | 10.8 | 0.000 | ||
RM×CT | 4 | 1.1 | 0.358 | 4 | 2.1 | 0.095 | 4 | 5.6 | 0.001 | ||
S×RM×CT | 8 | 1.5 | 0.177 | 8 | 1.9 | 0.064 | 8 | 1.5 | 0.171 |
投放方式 Releasing method | 覆盖处理 Coverage treatment | 辽东栎 Quercus wutaishanica | 野李 Prunus salicina | 华山松 Pinus armandii | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
PIS (%) | PAR (%) | HAR (%) | PIS (%) | PAR (%) | HAR (%) | PIS (%) | PAR (%) | HAR (%) | ||||
单独投放 Seperately releasing | 对照 Control | 15.7 ± 4.2 | 0 | 2.8 ± 4.8 | 0 | 11.1 ± 7.3 | 29.6 ± 20.5 | 0 | 23.1 ± 4.2 | 0.9 ± 1.6 | ||
凋落物覆盖 Litter coverage | 5.6 ± 4.8 | 50.0 ± 17.3 | 5.6 ± 2.8 | 0 | 0 | 24.1 ± 14.0 | 0.9 ± 1.6 | 55.6 ± 9.6 | 0.9 ± 1.6 | |||
土壤覆盖 Soil coverage | 23.1 ± 3.2 | 25.0 ± 4.8 | 8.3 ±.8.0 | 0 | 0 | 0 | 0.9 ± 1.6 | 33.3 ± 15.5 | 0 | |||
组合投放 Assembly releasing | 对照 Control | 4.6 ± 4.1 | 0.9 ± 2.3 | 13.9 ± 10.4 | 0 | 0 | 34.3 ± 16.3 | 0 | 8.3 ± 11.5 | 13.9 ± 16.0 | ||
凋落物覆盖 Litter coverage | 0.9 ± 2.3 | 28.7 ± 24.4 | 9.3 ± 7.6 | 0 | 9.3 ± 12.5 | 25.9 ± 18.8 | 0.9 ± 2.7 | 17.6 ± 21.2 | 3.7 ± 6.7 | |||
土壤覆盖 Soil coverage | 4.6 ± 7.4 | 26.9 ± 28.4 | 4.6 ± 5.5 | 0 | 42.6 ± 47.4 | 5.6 ± 7.0 | 0 | 7.4 ± 10.9 | 1.9 ± 2.9 | |||
混合投放 Blend releasing | 对照 Control | 0 | 0 | 2.8 ± 4.8 | 0 | 19.4 ± 9.6 | 25.0 ± 8.3 | 2.8 ± 4.8 | 36.1 ± 4.8 | 30.6 ± 4.8 | ||
凋落物覆盖 Litter coverage | 2.8 ± 4.8 | 27.8 ± 12.7 | 13.9 ± 12.7 | 0 | 58.3 ± 25.0 | 16.7 ± 8.3 | 2.8 ± 4.8 | 55.6 ± 9.6 | 5.6 ± 9.6 | |||
土壤覆盖 Soil coverage | 5.6 ± 4.8 | 8.3 ± 8.3 | 25.0 ± 16.7 | 0 | 11.1 ± 4.8 | 8.3 ± 8.3 | 0 | 25.0 ± 16.7 | 50.0 ± 8.3 |
表2 不同覆盖处理和投放方式下辽东栎、野李和华山松种子在六盘山区辽东栎幼林投放点的命运
Table 2 Fates of Quercus wutaishanica, Prunus salicina and Pinus armandii seeds in releasing plots of young Q. wutaishanica stands in Liupan Mountains under different coverage treatments and releasing methods
投放方式 Releasing method | 覆盖处理 Coverage treatment | 辽东栎 Quercus wutaishanica | 野李 Prunus salicina | 华山松 Pinus armandii | ||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
PIS (%) | PAR (%) | HAR (%) | PIS (%) | PAR (%) | HAR (%) | PIS (%) | PAR (%) | HAR (%) | ||||
单独投放 Seperately releasing | 对照 Control | 15.7 ± 4.2 | 0 | 2.8 ± 4.8 | 0 | 11.1 ± 7.3 | 29.6 ± 20.5 | 0 | 23.1 ± 4.2 | 0.9 ± 1.6 | ||
凋落物覆盖 Litter coverage | 5.6 ± 4.8 | 50.0 ± 17.3 | 5.6 ± 2.8 | 0 | 0 | 24.1 ± 14.0 | 0.9 ± 1.6 | 55.6 ± 9.6 | 0.9 ± 1.6 | |||
土壤覆盖 Soil coverage | 23.1 ± 3.2 | 25.0 ± 4.8 | 8.3 ±.8.0 | 0 | 0 | 0 | 0.9 ± 1.6 | 33.3 ± 15.5 | 0 | |||
组合投放 Assembly releasing | 对照 Control | 4.6 ± 4.1 | 0.9 ± 2.3 | 13.9 ± 10.4 | 0 | 0 | 34.3 ± 16.3 | 0 | 8.3 ± 11.5 | 13.9 ± 16.0 | ||
凋落物覆盖 Litter coverage | 0.9 ± 2.3 | 28.7 ± 24.4 | 9.3 ± 7.6 | 0 | 9.3 ± 12.5 | 25.9 ± 18.8 | 0.9 ± 2.7 | 17.6 ± 21.2 | 3.7 ± 6.7 | |||
土壤覆盖 Soil coverage | 4.6 ± 7.4 | 26.9 ± 28.4 | 4.6 ± 5.5 | 0 | 42.6 ± 47.4 | 5.6 ± 7.0 | 0 | 7.4 ± 10.9 | 1.9 ± 2.9 | |||
混合投放 Blend releasing | 对照 Control | 0 | 0 | 2.8 ± 4.8 | 0 | 19.4 ± 9.6 | 25.0 ± 8.3 | 2.8 ± 4.8 | 36.1 ± 4.8 | 30.6 ± 4.8 | ||
凋落物覆盖 Litter coverage | 2.8 ± 4.8 | 27.8 ± 12.7 | 13.9 ± 12.7 | 0 | 58.3 ± 25.0 | 16.7 ± 8.3 | 2.8 ± 4.8 | 55.6 ± 9.6 | 5.6 ± 9.6 | |||
土壤覆盖 Soil coverage | 5.6 ± 4.8 | 8.3 ± 8.3 | 25.0 ± 16.7 | 0 | 11.1 ± 4.8 | 8.3 ± 8.3 | 0 | 25.0 ± 16.7 | 50.0 ± 8.3 |
图2 辽东栎、野李和华山松种子在六盘山区辽东栎幼林被啮齿动物搬运后的取食和贮藏距离(平均值±SD)。同一命运类型不同物种间的不同字母表示差异显著。
Fig. 2 Seed predation and hoarding distances of Quercus wutaishanica(QW), Prunus salicina(PS) and Pinus armandii (PA) after removal by rodents in young Q. wutaishanica stands of Liupan Mountains. Different letters in different species within the same seed fate type indicate significant difference at P = 0.05 level.
图3 辽东栎、野李和华山松种子在六盘山区辽东栎幼林被啮齿动物搬运后取食(A)和贮藏(B)距离的分布频次
Fig. 3 Distribution frequency of predation (A) and hoarding (B) distance of Quercus wutaishanica, Prunus salicina and Pinus armandii seeds after removal by rodents in young Q. wutaishanica stands of Liupan Mountains.
取食点/贮藏点大小 Size of predation site/ cache site | 取食点 Predation site | 贮藏点 Cache site | |||||
---|---|---|---|---|---|---|---|
辽东栎 Quercus wutaishanica | 野李 Prunus salicina | 华山松 Pinus armandii | 辽东栎 Quercus wutaishanica | 野李 Prunus salicina | 华山松 Pinus armandii | ||
1 | 58 (82.9) | 3 (23.1) | 40 (62.5) | 53 (94.6) | 131 (94.2) | 39 (83.0) | |
2 | 2 (2.9) | 2 (15.4) | 7 (10.9) | 2 (3.6) | 4 (2.9) | 3 (6.4) | |
3 | 1 (1.4) | 1 (7.7) | 3 (4.7) | 1 (1.8) | 1 (0.7) | 3 (6.4) | |
4 | 3 (4.3) | 2 (15.4) | 3 (4.7) | - | 2 (1.4) | 1 (0.7) | |
5 | 1 (1.4) | - | - | - | 1 (0.7) | 1 (0.7) | |
6 | 1 (1.4) | - | - | - | - | - | |
7 | - | 1 (7.7) | 1 (1.6) | - | - | - | |
9 | - | - | 2 (3.1) | - | - | - | |
10 | - | - | 1 (1.6) | - | - | - | |
11 | - | - | 2 (3.1) | - | - | - | |
12 | - | - | 1 (1.6) | - | - | - | |
15 | 1 (1.4) | 1 (7.7) | - | - | - | - | |
19 | - | 1 (7.7) | 1 (1.6) | - | - | - | |
23 | - | - | 1 (1.6) | - | - | - | |
25 | - | - | 1 (1.6) | - | - | - | |
40 | 1 (1.4) | - | - | - | - | - | |
46 | 1 (1.4) | 1 (7.7) | 1 (1.6) | - | - | - | |
72 | 1 (1.4) | 1 (7.7) | - | - | - | - |
表3 辽东栎、野李和华山松种子被啮齿动物搬运后不同大小的取食点和贮藏点数量(括号内数字为占总数的百分比)
Table 3 Numbers of different size of seed predation site and cache site of Quercus wutaishanica, Prunus salicina and Pinus armandii after removal by rodents (The number in bracket is the percentage of total )
取食点/贮藏点大小 Size of predation site/ cache site | 取食点 Predation site | 贮藏点 Cache site | |||||
---|---|---|---|---|---|---|---|
辽东栎 Quercus wutaishanica | 野李 Prunus salicina | 华山松 Pinus armandii | 辽东栎 Quercus wutaishanica | 野李 Prunus salicina | 华山松 Pinus armandii | ||
1 | 58 (82.9) | 3 (23.1) | 40 (62.5) | 53 (94.6) | 131 (94.2) | 39 (83.0) | |
2 | 2 (2.9) | 2 (15.4) | 7 (10.9) | 2 (3.6) | 4 (2.9) | 3 (6.4) | |
3 | 1 (1.4) | 1 (7.7) | 3 (4.7) | 1 (1.8) | 1 (0.7) | 3 (6.4) | |
4 | 3 (4.3) | 2 (15.4) | 3 (4.7) | - | 2 (1.4) | 1 (0.7) | |
5 | 1 (1.4) | - | - | - | 1 (0.7) | 1 (0.7) | |
6 | 1 (1.4) | - | - | - | - | - | |
7 | - | 1 (7.7) | 1 (1.6) | - | - | - | |
9 | - | - | 2 (3.1) | - | - | - | |
10 | - | - | 1 (1.6) | - | - | - | |
11 | - | - | 2 (3.1) | - | - | - | |
12 | - | - | 1 (1.6) | - | - | - | |
15 | 1 (1.4) | 1 (7.7) | - | - | - | - | |
19 | - | 1 (7.7) | 1 (1.6) | - | - | - | |
23 | - | - | 1 (1.6) | - | - | - | |
25 | - | - | 1 (1.6) | - | - | - | |
40 | 1 (1.4) | - | - | - | - | - | |
46 | 1 (1.4) | 1 (7.7) | 1 (1.6) | - | - | - | |
72 | 1 (1.4) | 1 (7.7) | - | - | - | - |
图4 辽东栎、野李和华山松种子在六盘山区辽东栎幼林被啮齿动物搬运后不同贮藏方式和丢弃种子的百分比。同一贮藏类型(或丢弃)的不同物种间的不同字母表示差异显著。
Fig. 4 Seeds proportion of different hoarding / discarding types of Quercus wutaishanica (QW), Prunus salicina (PS) and Pinus armandii (PA) after removal by rodents in young Q. wutaishanica stands of Liupan Mountains. Different letters in different species within the same hoarding / discarding types indicate significant difference at P = 0.05 level.
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