Biodiv Sci ›› 2016, Vol. 24 ›› Issue (6): 639-648. DOI: 10.17520/biods.2015134
• Original Papers: Plant Diversity • Previous Articles Next Articles
Xiaojing Liu1, Siyuan Ren2, Luxin Li2, Yongzhong Ye2, Zhiliang Yuan2, Ting Wang2,*()
Received:
2016-02-15
Accepted:
2016-06-06
Online:
2016-06-20
Published:
2016-06-20
Contact:
Wang Ting
Xiaojing Liu, Siyuan Ren, Luxin Li, Yongzhong Ye, Zhiliang Yuan, Ting Wang. Detecting density dependence on tree survival in a deciduous broad- leaved forest in Baotianman National Nature Reserve[J]. Biodiv Sci, 2016, 24(6): 639-648.
径级 DBH size | 物种数 Number of species | 个体数 Number of individuals | 死亡数(死亡率) Number of mortality (mortality rate, %) | 新增数(增员率) Number of recruitment (recruitment rate, %) | |||
---|---|---|---|---|---|---|---|
2009 | 2014 | 2009 | 2014 | ||||
小径级 Small DBH size (1 cm ≤ DBH < 5 cm) | 54 | 46 | 1,538 | 1,091 | 482 (31.34) | 35 (2.28) | |
中径级 Medium DBH size (5 cm ≤ DBH < 10 cm) | 39 | 35 | 600 | 523 | 197 (32.83) | 120 (20.0) | |
大径级 Large DBH size (DBH ≥ 10 cm) | 22 | 24 | 417 | 381 | 68 (16.31) | 32 (7.68) | |
总计 Total (DBH ≥ 1 cm) | 58 | 53 | 2,555 | 1,995 | 747 (29.24) | 187 |
Table 1 Summary data of two census in a 1-ha deciduous broad-leaved forest plot in Baotianman National Nature Reserve in 2009 and 2014
径级 DBH size | 物种数 Number of species | 个体数 Number of individuals | 死亡数(死亡率) Number of mortality (mortality rate, %) | 新增数(增员率) Number of recruitment (recruitment rate, %) | |||
---|---|---|---|---|---|---|---|
2009 | 2014 | 2009 | 2014 | ||||
小径级 Small DBH size (1 cm ≤ DBH < 5 cm) | 54 | 46 | 1,538 | 1,091 | 482 (31.34) | 35 (2.28) | |
中径级 Medium DBH size (5 cm ≤ DBH < 10 cm) | 39 | 35 | 600 | 523 | 197 (32.83) | 120 (20.0) | |
大径级 Large DBH size (DBH ≥ 10 cm) | 22 | 24 | 417 | 381 | 68 (16.31) | 32 (7.68) | |
总计 Total (DBH ≥ 1 cm) | 58 | 53 | 2,555 | 1,995 | 747 (29.24) | 187 |
物种 Species | 拉丁名 Latin name | 重要值 IV | |
---|---|---|---|
2009 | 2014 | ||
槲栎 | Quercus aliena | 20.46 | 21.65 |
水榆花楸 | Sorbus alnifolia | 16.69 | 19.17 |
三桠乌药 | Lindera obtusiloba | 11.26 | 7.59 |
青榨槭 | Acer davidii | 9.62 | 10.88 |
野茉莉 | Styrax japonicus | 4.94 | 5.72 |
毛樱桃 | Cerasus tomentosa | 3.49 | 3.53 |
连翘 | Forsythia suspensa | 2.49 | 2.75 |
白檀 | Symplocos paniculata | 2.42 | 1.88 |
卫矛 | Euonymus alatus | 2.42 | 2.41 |
秦岭木姜子 | Litsea tsinlingensis | 2.38 | |
元宝槭 | Acer truncatum | 2.24 | 2.70 |
千金榆 | Carpinus cordata | 1.75 | 2.00 |
山梅花 | Philadelphus incanus | 1.59 | 1.35 |
暖木 | Meliosma veitchioru | 1.52 | 1.74 |
泡花树 | Meliosma cuneifolia | 1.44 | 1.59 |
马鞍树 | Maackia hupehensi | 1.55 | |
桦叶荚蒾 | Viburnum betulifolium | 1.32 | 1.59 |
四照花 | Dendrobenthamia japonica var. chinensis | 1.25 | 1.55 |
华东椴 | Tilia japonica | 1.06 | |
老鸹铃 | Styrax hemsleyanus | 1.02 | |
灯台树 | Bothrocaryum controversum | 0.94 | |
粉椴 | Tilia oliveri | 0.92 | |
其他 | Others | 10.12 | 9.03 |
Table 2 Importance value (IV) dynamics of top 20 species between 2009 and 2014 in a 1-ha deciduous broad-leaved forest plot in Baotianman National Nature Reserve
物种 Species | 拉丁名 Latin name | 重要值 IV | |
---|---|---|---|
2009 | 2014 | ||
槲栎 | Quercus aliena | 20.46 | 21.65 |
水榆花楸 | Sorbus alnifolia | 16.69 | 19.17 |
三桠乌药 | Lindera obtusiloba | 11.26 | 7.59 |
青榨槭 | Acer davidii | 9.62 | 10.88 |
野茉莉 | Styrax japonicus | 4.94 | 5.72 |
毛樱桃 | Cerasus tomentosa | 3.49 | 3.53 |
连翘 | Forsythia suspensa | 2.49 | 2.75 |
白檀 | Symplocos paniculata | 2.42 | 1.88 |
卫矛 | Euonymus alatus | 2.42 | 2.41 |
秦岭木姜子 | Litsea tsinlingensis | 2.38 | |
元宝槭 | Acer truncatum | 2.24 | 2.70 |
千金榆 | Carpinus cordata | 1.75 | 2.00 |
山梅花 | Philadelphus incanus | 1.59 | 1.35 |
暖木 | Meliosma veitchioru | 1.52 | 1.74 |
泡花树 | Meliosma cuneifolia | 1.44 | 1.59 |
马鞍树 | Maackia hupehensi | 1.55 | |
桦叶荚蒾 | Viburnum betulifolium | 1.32 | 1.59 |
四照花 | Dendrobenthamia japonica var. chinensis | 1.25 | 1.55 |
华东椴 | Tilia japonica | 1.06 | |
老鸹铃 | Styrax hemsleyanus | 1.02 | |
灯台树 | Bothrocaryum controversum | 0.94 | |
粉椴 | Tilia oliveri | 0.92 | |
其他 | Others | 10.12 | 9.03 |
种名 Species | 参数 Parameter | 邻体距离 Neighbourhood distance | ||
---|---|---|---|---|
5 m | 7.5 m | 10 m | ||
槲栎 Quercus aliena | CON | 0 | 0 | 0 |
HET | + | + | 0 | |
CONBA | +++ | + | 0 | |
HETBA | - - - | - - - | - - - | |
水榆花楸 Sorbus alnifolia | CON | +++ | +++ | +++ |
HET | - - - | - - - | - - - | |
CONBA | - - - | - - - | - - - | |
HETBA | +++ | +++ | +++ | |
青榨槭 Acer davidii | CON | 0 | 0 | 0 |
HET | 0 | 0 | 0 | |
CONBA | - - - | - - - | - - - | |
HETBA | 0 | 0 | 0 | |
三桠乌药 Lindera obtusiloba | CON | 0 | + | ++ |
HET | - | - | - | |
CONBA | - - | - - | - - | |
HETBA | 0 | 0 | 0 | |
野茉莉 Styrax japonicus | CON | - - - | - - - | - - - |
HET | 0 | 0 | 0 | |
CONBA | - | - | - | |
HETBA | + | 0 | 0 | |
元宝槭 Acer truncatum | CON | 0 | 0 | 0 |
HET | - - | - | - - | |
CONBA | 0 | - | - - | |
HETBA | 0 | 0 | 0 | |
毛樱桃 Cerasus tomentosa | CON | - - | - - | - |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | - | |
HETBA | 0 | 0 | 0 | |
白檀 Symplocos paniculata | CON | 0 | 0 | 0 |
HET | 0 | 0 | 0 | |
CONBA | - | - - | - - | |
HETBA | 0 | 0 | 0 | |
秦岭木姜子 Litsea tsinlingensis | CON | 0 | 0 | 0 |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | 0 | |
HETBA | ++ | + | 0 | |
千金榆 Carpinus cordata | CON | 0 | - | - - |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | 0 | |
HETBA | 0 | 0 | 0 | |
暖木 Meliosma veitchiorum | CON | - - | - - - | - - |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | 0 | |
HETBA | 0 | 0 | + |
Table 3 Result of neighborhood analysis for different scales with different species in a 1-ha deciduous broad-leaved forest plot in Baotianman National Nature Reserve
种名 Species | 参数 Parameter | 邻体距离 Neighbourhood distance | ||
---|---|---|---|---|
5 m | 7.5 m | 10 m | ||
槲栎 Quercus aliena | CON | 0 | 0 | 0 |
HET | + | + | 0 | |
CONBA | +++ | + | 0 | |
HETBA | - - - | - - - | - - - | |
水榆花楸 Sorbus alnifolia | CON | +++ | +++ | +++ |
HET | - - - | - - - | - - - | |
CONBA | - - - | - - - | - - - | |
HETBA | +++ | +++ | +++ | |
青榨槭 Acer davidii | CON | 0 | 0 | 0 |
HET | 0 | 0 | 0 | |
CONBA | - - - | - - - | - - - | |
HETBA | 0 | 0 | 0 | |
三桠乌药 Lindera obtusiloba | CON | 0 | + | ++ |
HET | - | - | - | |
CONBA | - - | - - | - - | |
HETBA | 0 | 0 | 0 | |
野茉莉 Styrax japonicus | CON | - - - | - - - | - - - |
HET | 0 | 0 | 0 | |
CONBA | - | - | - | |
HETBA | + | 0 | 0 | |
元宝槭 Acer truncatum | CON | 0 | 0 | 0 |
HET | - - | - | - - | |
CONBA | 0 | - | - - | |
HETBA | 0 | 0 | 0 | |
毛樱桃 Cerasus tomentosa | CON | - - | - - | - |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | - | |
HETBA | 0 | 0 | 0 | |
白檀 Symplocos paniculata | CON | 0 | 0 | 0 |
HET | 0 | 0 | 0 | |
CONBA | - | - - | - - | |
HETBA | 0 | 0 | 0 | |
秦岭木姜子 Litsea tsinlingensis | CON | 0 | 0 | 0 |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | 0 | |
HETBA | ++ | + | 0 | |
千金榆 Carpinus cordata | CON | 0 | - | - - |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | 0 | |
HETBA | 0 | 0 | 0 | |
暖木 Meliosma veitchiorum | CON | - - | - - - | - - |
HET | 0 | 0 | 0 | |
CONBA | 0 | 0 | 0 | |
HETBA | 0 | 0 | + |
模型类型 Model type | 邻体距离 Neighbourhood distance | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
5 m | 7.5 m | 10 m | ||||||||||
小 Small | 中 Medium | 大 Large | 小 Small | 中 Medium | 大 Large | 小 Small | 中 Medium | 大 Large | ||||
基本模型 Basic model | d+n+h+(sp+20s)random | 1,484.06 | 355.5304 | 380.3177 | 1,483.798 | 355.0877 | 372.4036 | 1,484.64 | 359.2236 | 373.3339 | ||
d+c+b+(sp+20s)random | 1,480.921 | 355.6752 | 378.72 | 1,482.687 | 355.3472 | 371.565 | 1,479.719 | 355.676 | 371.266 | |||
d+n+h+c+b+(sp+20s)random | 1,483.84 | 359.2017 | 381.6294 | 1,485.789 | 358.0195 | 370.1479 | 1,483.541 | 357.485 | 369.087 | |||
d+n+h+c+b+i+(sp+20s)random | 1,485.83 | 356.6697 | 379.306 | 1,487.509 | 356.979 | 372.125 | 1,485.34 | 357.0264 | 370.084 | |||
交互作用 模型 Interaction model | d*(n+h) +(sp+20s)random | 1,484.249 | 359.3985 | 382.5019 | 1,485.738 | 358.9014 | 374.9681 | 1,486.79 | 358.066 | 375.3167 | ||
d*(n+h+i) +(sp+20s)random | 1,488.12 | 359.3586 | 384.9341 | 1,489.323 | 362.611 | 378.8982 | 1,489.957 | 361.7479 | 378.8444 | |||
d*(c+b) +(sp+20s)random | 1,475.82 | 358.6642 | 378.6484 | 1,479.193 | 357.8086 | 375.5305 | 1,481.48 | 359.2018 | 374.0463 | |||
d*(c+b+i) +(sp+20s)random | 1,479.6 | 358.9814 | 380.8261 | 1,473.86 | 361.5722 | 379.2916 | 1,481.13 | 363.1487 | 377.7625 | |||
d*(n+h+c+b) +(sp+20s)random | 1,480.32 | 366.2005 | 383.7345 | 1,475.386 | 365.396 | 377.4086 | 1,479.243 | 375.7429 | 375.7429 | |||
d*(n+h+c+b+i) +(sp+20s)random | 1,474.3 | 366.2815 | 386.4617 | 1,474.083 | 369.1937 | 381.3527 | 1,480.58 | 368.7947 | 379.6699 |
Table 4 AIC values of different GLMMs (generalized linear mixed models) at three scales (r) in a 1-ha deciduous broad-leaved forest plot in Baotianman National Nature Reserve
模型类型 Model type | 邻体距离 Neighbourhood distance | |||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|
5 m | 7.5 m | 10 m | ||||||||||
小 Small | 中 Medium | 大 Large | 小 Small | 中 Medium | 大 Large | 小 Small | 中 Medium | 大 Large | ||||
基本模型 Basic model | d+n+h+(sp+20s)random | 1,484.06 | 355.5304 | 380.3177 | 1,483.798 | 355.0877 | 372.4036 | 1,484.64 | 359.2236 | 373.3339 | ||
d+c+b+(sp+20s)random | 1,480.921 | 355.6752 | 378.72 | 1,482.687 | 355.3472 | 371.565 | 1,479.719 | 355.676 | 371.266 | |||
d+n+h+c+b+(sp+20s)random | 1,483.84 | 359.2017 | 381.6294 | 1,485.789 | 358.0195 | 370.1479 | 1,483.541 | 357.485 | 369.087 | |||
d+n+h+c+b+i+(sp+20s)random | 1,485.83 | 356.6697 | 379.306 | 1,487.509 | 356.979 | 372.125 | 1,485.34 | 357.0264 | 370.084 | |||
交互作用 模型 Interaction model | d*(n+h) +(sp+20s)random | 1,484.249 | 359.3985 | 382.5019 | 1,485.738 | 358.9014 | 374.9681 | 1,486.79 | 358.066 | 375.3167 | ||
d*(n+h+i) +(sp+20s)random | 1,488.12 | 359.3586 | 384.9341 | 1,489.323 | 362.611 | 378.8982 | 1,489.957 | 361.7479 | 378.8444 | |||
d*(c+b) +(sp+20s)random | 1,475.82 | 358.6642 | 378.6484 | 1,479.193 | 357.8086 | 375.5305 | 1,481.48 | 359.2018 | 374.0463 | |||
d*(c+b+i) +(sp+20s)random | 1,479.6 | 358.9814 | 380.8261 | 1,473.86 | 361.5722 | 379.2916 | 1,481.13 | 363.1487 | 377.7625 | |||
d*(n+h+c+b) +(sp+20s)random | 1,480.32 | 366.2005 | 383.7345 | 1,475.386 | 365.396 | 377.4086 | 1,479.243 | 375.7429 | 375.7429 | |||
d*(n+h+c+b+i) +(sp+20s)random | 1,474.3 | 366.2815 | 386.4617 | 1,474.083 | 369.1937 | 381.3527 | 1,480.58 | 368.7947 | 379.6699 |
Fig. 2 Neighbourhood effects of conspecific neighburs (CON), heterospecific neighburs (HET) and neighborhood relatedness index (NRI) on individual survivalSmall, medium and large indicate small DBH class (1 cm ≤ DBH < 5 cm), medium DBH class (5 cm ≤ DBH < 10 cm) and large DBH class (DBH ≥ 10 cm), respectively. The 5 m, 7.5 m and 10 m indicate different neighbourhood scales. ○, ●, ■ indicate correlations at P > 0.05, P < 0.05 and P < 0.01 level, respectively.
Fig. 3 Neighbourhood effects of individual trees with different DBH size and different scales on survivalA, B and C mean different size with small (1 cm ≤ DBH < 5 cm), medium (5 cm ≤ DBH < 10 cm) and large (DBH ≥ 10 cm) DBH, respectively. The number 1, 2, 3 indicate different neighbourhood scales of 5 m, 7.5 m and 10 m. ○ mean no significance correlation (P > 0.05), and ●、▲、■ indicate different significant correlations at p-vale as 0.05, 0.01 and 0.001, respectively.
[1] | Bagchi R, Gallery RE, Gripenberg S, Gurr SJ, Narayan L, Addis CE, Freckleton RP, Lewis OT (2014) Pathogens and insect herbivores drive rainforest plant diversity and composition. Nature, 506, 85-88. |
[2] | Bagchi R, Press MC, Scholes JD (2010) Evolutionary history and distance dependence control survival of dipterocarp seedlings. Ecology Letters, 13, 51-59. |
[3] | Bell T, Freckleton RP, Lewis OT (2006) Plant pathogens drive density-dependent seedling mortality in a tropical tree. Ecology Letters, 9, 569-574. |
[4] | Bremer B, Bremer K, Chase M, Fay M, Reveal J, Soltis D, Soltis P, Stevens P (2009) An update of the Angiosperm Phylogeny Group classification for the orders and families of flowering plants: APG III. Botanical Journal of the Linnean Society, 161, 105-121. |
[5] | Burnham KP, Anderson DR (2002) Model selection and multimodel inference: a practical information-theoretic approach. Journal of Wildlife Management, 67, 606. |
[6] | Condit R (1995) Research in large, long-term tropical forest plots. Trends in Ecology & Evolution, 10, 18-22. |
[7] | Condit R, Ashton PS, Manokaran N, LaFrankie JV, Hubbell SP, Foster RB (1999) Dynamics of the forest communities at Pasoh and Barro Colorado: comparing two 50-ha plots. Philosophical Transactions of the Royal Society of London Series B: Biological Sciences, 354, 1739-1748. |
[8] | Connell JH (1970) On the role of natural enemies in preventing competitive exclusion in some marine animals and in forest trees. Center Ag Publishing & Documentation Wageningen, 298, 298-312. |
[9] | Gilbert GS, Webb CO (2007) Phylogenetic signal in plant pathogen-host range. Proceedings of the National Academy of Sciences, USA, 104, 4979-4983. |
[10] | Gonzalez MA, Roger Al, Courtois EA, Jabot F, Norden N, Paine CET, Baraloto C, Thébaud C, Chave Jrm (2010) Shifts in species and phylogenetic diversity between sapling and tree communities indicate negative density dependence in a lowland rain forest. Journal of Ecology, 98, 137-146. |
[11] | Harms KE, Wright SJ, Calderon O, Hernandez A, Herre EA (2000) Pervasive density-dependent recruitment enhances seedling diversity in a tropical forest. Nature, 404, 493-495. |
[12] | Harms KE, Condit R, Hubbell SP, Foster RB (2001) Habitat associations of trees and shrubs in a 50-ha Neotropical forest plot. Journal of Ecology, 89, 947-959. |
[13] | He FL, Duncan RP (2000) Density-dependent effects on tree survival in an old-growth Douglas fir forest. Journal of Ecology, 88, 676-688. |
[14] | Hubbell SP (1980) Seed predation and the coexistence of tree species in tropical forests. Oikos, 35, 214-229. |
[15] | Hubbell SP (2001) The Unified Neutral Theory of Biodiversity and Biogeography (Vol. 32). Princeton University Press, Princeton. |
[16] | Janzen DH (1970) Herbivores and the number of tree species in tropical forests. The American Naturalist, 104, 501-528. |
[17] | John R, Dalling JW, Harms KE, Yavitt JB, Stallard RF, Mirabello M, Hubbell SP, Valencia R, Navarrete H, Vallejo M (2007) Soil nutrients influence spatial distributions of tropical tree species. Proceedings of the National Academy of Sciences, USA, 104, 864-869. |
[18] | Kembel SW, Hubbell SP (2006) The phylogenetic structure of a neotropical forest tree community. Ecology, 87, S86-S99. |
[19] | Lewis SL, Phillips OL, Sheil D, Vinceti B, Baker TR, Brown S, Graham AW, Higuchi N, Hilbert DW, Laurance WF, Lejoly J, Malhi Y, Monteagudo A, Vargas PN, Sonke B, Supardi N, Terborgh JW, Martínez RV (2004) Tropical forest tree mortality, recruitment and turnover rates: calculation, interpretation and comparison when census intervals vary. Journal of Ecology, 92, 929-944. |
[20] | Liu XB, Liang M, Etienne RS, Wang Y, Staehelin C, Yu SX (2012) Experimental evidence for a phylogenetic Janzen-Connell effect in a subtropical forest. Ecology Letters, 15, 111-118. |
[21] | Matos DMS, Freckleton RP, Watkinson AR (1999) The role of density dependence in the population dynamics of a tropical palm. Ecology, 80, 2635-2650. |
[22] | Metz MR, Sousa WP, Valencia R (2010) Widespread density-dependent seedling mortality promotes species coexistence in a highly diverse Amazonian rain forest. Ecology, 91, 3675-3685. |
[23] | Peters HA (2003) Neighbour-regulated mortality: the influence of positive and negative density dependence on tree populations in species-rich tropical forests. Ecology Letters, 6, 757-765. |
[24] | Piao TF, Comita LS, Jin GZ, Kim JH (2013) Density dependence across multiple life stages in a temperate old-growth forest of Northeast China. Oecologia, 172, 207-217. |
[25] | Pigot AL, Leather SR (2008) Invertebrate predators drive distance-dependent patterns of seedling mortality in a temperate tree Acer pseudoplatanus. Oikos, 117, 521-530. |
[26] | Tilman D (1994) Competition and biodiversity in spatially structured habitats. Ecology, 75, 2-16. |
[27] | Uriarte M, Swenson NG, Chazdon RL, Comita LS, Kress WJ, Erickson D, Forero-Montaña J, Zimmerman JK, Thompson J (2010) Trait similarity, shared ancestry and the structure of neighbourhood interactions in a subtropical wet forest: im-plications for community assembly. Ecology Letters, 13, 1503-1514. |
[28] | Volkov I, Banavar JR, He F, Hubbell SP, Maritan A (2005) Density dependence explains tree species abundance and diversity in tropical forests. Nature, 438, 658-661. |
[29] | Wang YH, Mi XC, Chen SW, Li MH,Yu MJ (2011) Regeneration dynamics of major tree species during 2002-2007 in a subtropical evergreen broad-leaved forest in Gutianshan National Nature Reserve in East China. Biodiversity Science, 19, 178-189. (in Chinese with English abstract) |
[汪殷华, 米湘成, 陈声文, 李铭红, 于明坚 (2011) 古田山常绿阔叶林主要树种2002-2007年间更新动态. 生物多样性, 19, 178-189.] | |
[30] | Webb CO, Ackerly DD, Kembel SW (2008) Phylocom: software for the analysis of phylogenetic community structure and trait evolution. Bioinformatics, 24, 2098-2100. |
[31] | Webb CO, Donoghue MJ (2005) Phylomatic: tree assembly for applied phylogenetics. Molecular Ecology Notes, 5, 181-183. |
[32] | Webb CO, Gilbert GS, Donoghue MJ (2006) Phylodiversity-dependent seedling mortality, size structure, and disease in a Bornean rain forest. Ecology, 87, S123-S131. |
[33] | White PS, Pickett ST (1985) Natural disturbance and patch dynamics: an introduction. in: The Ecology of Natural Disturbance and Patch Dynamics (eds Pickett ST, White PS), pp. 3-13. Academic Press, London. |
[34] | Zhang ZM, Zhu XL, Ye YZ, Liu XJ, Yao S, Mei SX (2010) Studies on fine root biomass of the Quercus communities in Baotianman National Nature Reserve. Journal of Henan Agricultural University, 44, 210-216.(in Chinese with English abstract) |
[张志铭, 朱学灵, 叶永忠, 刘晓静, 姚松, 梅世秀(2010) 宝天曼自然保护区栎类群落细根生物量的研究. 河南农业大学学报, 44, 210-216.] | |
[35] | Zhu Y, Comita LS, Hubbell SP, Ma KP (2015) Conspecific and phylogenetic density-dependent survival differs across life stages in a tropical forest. Journal of Ecology, 103, 957-966. |
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