Chin J Plant Ecol ›› 2007, Vol. 31 ›› Issue (3): 425-430.DOI: 10.17521/cjpe.2007.0051
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YANG Juan1, GE Jian-Ping2,*(), LIU Li-Juan2, DING Yi3, TAN Ying-Chun4
Received:
2006-03-15
Accepted:
2006-07-31
Online:
2007-03-15
Published:
2007-05-30
Contact:
GE Jian-Ping
YANG Juan, GE Jian-Ping, LIU Li-Juan, DING Yi, TAN Ying-Chun. GAP-PHASE REGENERATION RULES OF CONIFER-BROADLEAVED MIXED FOREST IN WOLONG NATURE RESERVE, CHINA[J]. Chin J Plant Ecol, 2007, 31(3): 425-430.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2007.0051
林隙干扰特征 Gap disturbance characteristics | 海拔 Elevation | 坡度 Slope angle | 坡向 Aspect | |
---|---|---|---|---|
林隙大小特征 Gap size characteristics | EG | 0.094 | -0.192 | 0.111 |
CG | 0.050 | -0.083 | 0.167 | |
Dcg/H | 0.091 | -0.105 | 0.183 | |
形成木特征 Gap maker characteristics | GMn | -0.152 | 0.231 | 0.304* |
SPn | -0.115 | 0.197 | 0.144 | |
Smax | 0.156 | -0.153 | -0.182 | |
Stol | 0.122 | -0.122 | 0.023 | |
林隙形成方式 Gap forming manners | DM | -0.135 | 0.226 | 0.142 |
KF | 0.297* | -0.168 | 0.046 | |
GB | -0.236 | 0.295* | 0.175 | |
ZG | -0.219 | -0.033 | 0.031 | |
KL | -0.011 | 0.153 | 0.186 |
Table 1 Pearson correlations between gap disturbance characteristics and topographic factors
林隙干扰特征 Gap disturbance characteristics | 海拔 Elevation | 坡度 Slope angle | 坡向 Aspect | |
---|---|---|---|---|
林隙大小特征 Gap size characteristics | EG | 0.094 | -0.192 | 0.111 |
CG | 0.050 | -0.083 | 0.167 | |
Dcg/H | 0.091 | -0.105 | 0.183 | |
形成木特征 Gap maker characteristics | GMn | -0.152 | 0.231 | 0.304* |
SPn | -0.115 | 0.197 | 0.144 | |
Smax | 0.156 | -0.153 | -0.182 | |
Stol | 0.122 | -0.122 | 0.023 | |
林隙形成方式 Gap forming manners | DM | -0.135 | 0.226 | 0.142 |
KF | 0.297* | -0.168 | 0.046 | |
GB | -0.236 | 0.295* | 0.175 | |
ZG | -0.219 | -0.033 | 0.031 | |
KL | -0.011 | 0.153 | 0.186 |
Fig.1 Relative predominance comparison between regenerative seedlings and gap makers 1. 岷江冷杉 Abies faxoniana 2. 桦木 Betula spp. 3. 铁杉 Tsuga chinensis 4. 杜鹃Rhododendron spp. 5. 麦吊杉Picea brachytyla 6. 西南樱桃Prunus pilosiuscula 7. 槭树Acer spp. 8. 华山松 Pinus armandi
岷江冷杉2) | 铁杉3) | 杜鹃4) | |
---|---|---|---|
桦木1) | 0.258 | -0.089 | -0.124 |
岷江冷杉2) | 0.292* | 0.056 | |
铁杉3) | 0.060 |
Table 2 Spearman correlation between gap regenerative species
岷江冷杉2) | 铁杉3) | 杜鹃4) | |
---|---|---|---|
桦木1) | 0.258 | -0.089 | -0.124 |
岷江冷杉2) | 0.292* | 0.056 | |
铁杉3) | 0.060 |
更新物种 Regeneration species | PC1 | PC2 | PC3 | PC4 | PC5 |
---|---|---|---|---|---|
桦木1) | -0.048 | -0.011 | -0.275* | 0.010 | -0.048 |
岷江冷杉2) | -0.111 | 0.563** | -0.143 | -0.079 | -0.210 |
铁杉3) | -0.024 | -0.056 | 0.093 | -0.020 | 0.121 |
杜鹃4) | -0.048 | 0.196 | 0.351** | 0.298* | 0.025 |
Table 4 Pearson correlations between the abundance of regenerative species and principal components of environmental factors
更新物种 Regeneration species | PC1 | PC2 | PC3 | PC4 | PC5 |
---|---|---|---|---|---|
桦木1) | -0.048 | -0.011 | -0.275* | 0.010 | -0.048 |
岷江冷杉2) | -0.111 | 0.563** | -0.143 | -0.079 | -0.210 |
铁杉3) | -0.024 | -0.056 | 0.093 | -0.020 | 0.121 |
杜鹃4) | -0.048 | 0.196 | 0.351** | 0.298* | 0.025 |
多样性指标 Biodiversity indexes | PC1 | PC2 | PC3 | PC4 | PC5 |
---|---|---|---|---|---|
H' | -0.075 | -0.271* | -0.071 | 0.002 | 0.173 |
MI | -0.101 | -0.055 | -0.077 | 0.089 | 0.329* |
J | 0.115 | -0.401* | -0.054 | -0.265 | -0.028 |
C | 0.004 | 0.328* | -0.076 | 0.054 | -0.112 |
TRS | 0.016 | 0.082 | 0.227 | 0.242 | 0.294* |
R | -0.188 | 0.054 | 0.172 | 0.176 | 0.290* |
Table 5 Pearson correlations between the biodiversity indexes of regenerative species and principal components of environmental factors
多样性指标 Biodiversity indexes | PC1 | PC2 | PC3 | PC4 | PC5 |
---|---|---|---|---|---|
H' | -0.075 | -0.271* | -0.071 | 0.002 | 0.173 |
MI | -0.101 | -0.055 | -0.077 | 0.089 | 0.329* |
J | 0.115 | -0.401* | -0.054 | -0.265 | -0.028 |
C | 0.004 | 0.328* | -0.076 | 0.054 | -0.112 |
TRS | 0.016 | 0.082 | 0.227 | 0.242 | 0.294* |
R | -0.188 | 0.054 | 0.172 | 0.176 | 0.290* |
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