植物生态学报 ›› 2026, Vol. 50 ›› Issue (2): 256-267.DOI: 10.17521/cjpe.2025.0248 cstr: 32100.14.cjpe.2025.0248
叶学敏1, 高伟1, 唐星林1, 陈伏生2, 孙荣喜2, 罗坤水1,*(
)
收稿日期:2025-06-30
接受日期:2025-12-13
出版日期:2026-02-28
发布日期:2026-04-01
通讯作者:
*罗坤水 (526492282@qq.com)基金资助:
YE Xue-Min1, GAO Wei1, TANG Xing-Lin1, CHEN Fu-Sheng2, SUN Rong-Xi2, LUO Kun-Shui1,*(
)
Received:2025-06-30
Accepted:2025-12-13
Online:2026-02-28
Published:2026-04-01
Contact:
*LUO Kun-Shui (526492282@qq.com)Supported by:摘要:
亚热带森林中, 昆虫取食会导致叶片损伤, 但氮磷添加是否能改变幼树的抗虫能力尚不明确。该研究以江西九连山常绿阔叶林的6种优势树种幼树为研究对象, 开展为期8年的氮磷添加实验, 测定不同处理下叶片的植食损伤率、化学计量比、机械抗性及化学抗性, 分析氮磷添加对幼树抗虫性的影响。结果表明, 幼树表现出较强的抗虫能力, 叶片平均植食损伤率为5.4%, 且损伤率不受氮添加、磷添加或氮磷共同添加处理的影响, 但存在显著树种差异, 且喜光树种显著高于耐阴树种。氮添加和氮磷共同添加显著提高了叶片氮含量, 却未显著改变叶片化学计量比; 磷添加显著增加了叶片磷含量并降低了叶片碳磷比。氮磷添加对叶片撕裂力和穿透力无显著影响, 相比之下, 氮添加诱导氨基酸含量显著上升, 磷添加提高了总酚含量, 单宁含量则保持稳定。值得注意的是, 喜光树种因叶片氮含量更高而更易受害, 而耐阴树种则表现出更低的损伤率, 并在机械抗性和化学防御方面更强。综上所述, 亚热带森林幼树通过稳定的物理防御和可塑的化学防御机制, 维持对背景性植食压力的较强抵抗力, 这有助于在全球变化背景下增强群落天然更新的稳定性。
叶学敏, 高伟, 唐星林, 陈伏生, 孙荣喜, 罗坤水. 氮磷添加对常绿阔叶林幼树叶片植食损伤的影响及调控机制. 植物生态学报, 2026, 50(2): 256-267. DOI: 10.17521/cjpe.2025.0248
YE Xue-Min, GAO Wei, TANG Xing-Lin, CHEN Fu-Sheng, SUN Rong-Xi, LUO Kun-Shui. Effects of nitrogen and phosphorus additions on leaf herbivory damage and its underlying mechanisms in saplings in an evergreen broad-leaved forest. Chinese Journal of Plant Ecology, 2026, 50(2): 256-267. DOI: 10.17521/cjpe.2025.0248
| 物种 Species | 合计 Total | 取样个体数量 Number of sampled individuals | |||
|---|---|---|---|---|---|
| 对照 Control | 氮添加 Nitrogen (N) addition | 磷添加 Phosphorus (P) addition | 氮磷共同添加 Combined N + P | ||
| 木荷 Schima superba | 115 | 30 | 29 | 29 | 27 |
| 短序润楠 Machilus breviflora | 81 | 19 | 24 | 21 | 17 |
| 绒毛润楠 M. velutina | 85 | 22 | 24 | 23 | 16 |
| 丝栗栲 Castanopsis fargesii | 83 | 23 | 21 | 16 | 23 |
| 米槠 C. carlesii | 76 | 19 | 16 | 26 | 15 |
| 甜槠 C. eyrei | 68 | 20 | 15 | 18 | 15 |
| 幼树 Saplings | 508 | 133 | 129 | 133 | 113 |
表1 叶片植食损伤率测定的物种及个体数量
Table 1 Number of individuals of different species measured by leaf herbivorous damage rate
| 物种 Species | 合计 Total | 取样个体数量 Number of sampled individuals | |||
|---|---|---|---|---|---|
| 对照 Control | 氮添加 Nitrogen (N) addition | 磷添加 Phosphorus (P) addition | 氮磷共同添加 Combined N + P | ||
| 木荷 Schima superba | 115 | 30 | 29 | 29 | 27 |
| 短序润楠 Machilus breviflora | 81 | 19 | 24 | 21 | 17 |
| 绒毛润楠 M. velutina | 85 | 22 | 24 | 23 | 16 |
| 丝栗栲 Castanopsis fargesii | 83 | 23 | 21 | 16 | 23 |
| 米槠 C. carlesii | 76 | 19 | 16 | 26 | 15 |
| 甜槠 C. eyrei | 68 | 20 | 15 | 18 | 15 |
| 幼树 Saplings | 508 | 133 | 129 | 133 | 113 |
图1 常绿阔叶林幼树叶片植食损伤率对氮磷添加的响应(A)及种间差异(B)。不同小写字母表示不同处理或不同物种间存在显著差异(p < 0.05), ***表示喜光树种和耐阴树种存在显著差异(p < 0.001)。
Fig. 1 Responses of leaf herbivorous damage rate of saplings to nitrogen and phosphorus addition (A), interspecific differences (B) in an evergreen broad-leaved forest. Different lowercase letters indicate differences among different treatments or species (p < 0.05), *** indicate differences between light-demaning species and shade-tolerant species (p < 0.001). +N, nitrogen addition; +P, phosphorus addition; N+P, nitrogen and phosphorus combined addition.
| LMM | LHDR | p | LMM | LHDR | p | LMM | LHDR | p |
|---|---|---|---|---|---|---|---|---|
| 固定效应 Fixed effect | 物种 Species | <0.001 | 固定效应 Fixed effect | 叶片大小 Leaf size | 0.002 | 固定效应 Fixed effect | 株高 Height | 0.004 |
| 氮添加 N | 0.289 | 氮添加 N | 0.123 | 氮添加 N | 0.265 | |||
| 磷添加 P | 0.217 | 磷添加 P | 0.209 | 磷添加 P | 0.209 | |||
| N × P | 0.998 | N × P | 0.717 | N × P | 0.635 | |||
| N × species | 0.052 | N × leaf size | 0.003 | N × height | 0.018 | |||
| P × species | 0.724 | P × leaf size | 0.836 | P × height | 0.544 | |||
| N × P × species | 0.756 | N × P × leaf size | 0.089 | N × P × height | 0.758 | |||
| 模型解释度 Model statistics | R2m | 0.141 | 模型解释度 Model statistics | R2m | 0.048 | 模型解释度 Model statistics | R2m | 0.034 |
| R2c | 0.141 | R2c | 0.048 | R2c | 0.034 |
表2 氮磷添加对常绿阔叶林中6种优势树种幼树叶片植食损伤率(LHDR)的线性混合模型(LMM)分析
Table 2 Linear mixed model (LMM) analysis for leaf herbivorous damage rate (LHDR) of six dominant tree species in an evergreen broad-leaved forest treated with nitrogen and phosphorus addition
| LMM | LHDR | p | LMM | LHDR | p | LMM | LHDR | p |
|---|---|---|---|---|---|---|---|---|
| 固定效应 Fixed effect | 物种 Species | <0.001 | 固定效应 Fixed effect | 叶片大小 Leaf size | 0.002 | 固定效应 Fixed effect | 株高 Height | 0.004 |
| 氮添加 N | 0.289 | 氮添加 N | 0.123 | 氮添加 N | 0.265 | |||
| 磷添加 P | 0.217 | 磷添加 P | 0.209 | 磷添加 P | 0.209 | |||
| N × P | 0.998 | N × P | 0.717 | N × P | 0.635 | |||
| N × species | 0.052 | N × leaf size | 0.003 | N × height | 0.018 | |||
| P × species | 0.724 | P × leaf size | 0.836 | P × height | 0.544 | |||
| N × P × species | 0.756 | N × P × leaf size | 0.089 | N × P × height | 0.758 | |||
| 模型解释度 Model statistics | R2m | 0.141 | 模型解释度 Model statistics | R2m | 0.048 | 模型解释度 Model statistics | R2m | 0.034 |
| R2c | 0.141 | R2c | 0.048 | R2c | 0.034 |
图2 常绿阔叶林幼树叶片化学计量比对氮磷添加的响应。不同小写字母表示不同处理间存在显著差异(p < 0.05)。CK, 对照; +N, 氮添加; +P, 磷添加; N+P, 氮磷共同添加。
Fig. 2 Responses of leaf stoichiometry of saplings to nitrogen and phosphorus addition in an evergreen broad-leaved forest. Different lowercase letters indicate differences among different treatments (p < 0.05). CK, control; +N, nitrogen addition; +P, phosphorus addition; N+P, nitrogen and phosphorus combined addition. Cmass, carbon content per unit mass; Nmass, nitrogen content per unit mass; Pmass, phosphorus content per unit mass.
图3 常绿阔叶林幼树比叶质量(LMA)和叶片机械抗性对氮磷添加的响应。不同小写字母表示不同处理间存在显著差异(p < 0.05)。CK, 对照; +N, 氮添加; +P, 磷添加; N+P, 氮磷共同添加。
Fig. 3 Responses of leaf mass per area (LMA) and leaf mechanical resistance of saplings to nitrogen and phosphorus addition in an evergreen broad-leaved forest. Different lowercase letters indicate differences among different treatments (p < 0.05). CK, control; +N, nitrogen addition; +P, phosphorus addition; N+P, nitrogen and phosphorus combined addition. Fp, leaf force to punch; Ft, leaf force to tear.
图4 常绿阔叶林幼树叶片化学抗性对氮磷添加的响应。不同小写字母表示不同处理间存在显著差异(p < 0.05)。CK, 对照; +N, 氮添加; +P, 磷添加; N+P, 氮磷共同添加。
Fig. 4 Responses of leaf chemical resistance of saplings to nitrogen and phosphorus addition in an evergreen broad-leaved forest. Different lowercase letters indicate differences among different treatments (p < 0.05). CK, control; +N, nitrogen addition; +P, phosphorus addition; N+P, nitrogen and phosphorus combined addition. AA, amino acid content; TA, tannin content; TPh, total phenolic content.
| 叶片性状 Leaf trait | 喜光树种 Light-demanding species | 耐阴树种 Shadow-tolerant species | p |
|---|---|---|---|
| 叶片植食损伤率 LHDR (%) | 7.13 ± 0.51 | 3.38 ± 0.28 | *** |
| 单位质量碳含量 Cmass (mg·g-1) | 478.19 ± 2.47 | 480.20 ± 3.04 | 0.22 |
| 单位质量氮含量 Nmass (mg·g-1) | 15.71 ± 0.32 | 13.79 ± 0.27 | *** |
| 单位质量磷含量 Pmass (mg·g-1) | 0.864 ± 0.026 | 0.824 ± 0.022 | 0.18 |
| C:N | 31.20 ± 0.67 | 35.79 ± 0.83 | *** |
| C:P | 622.2 ± 24.0 | 637.1 ± 20.7 | 0.54 |
| N:P | 19.70 ± 0.78 | 17.78 ± 0.57 | 0.13 |
| 比叶质量 LMA (g·m-2) | 89.44 ± 3.17 | 96.31 ± 3.36 | 0.06 |
| 叶片撕裂力 Ft (KN·m-1) | 0.299 ± 0.007 | 0.402 ± 0.009 | *** |
| 叶片穿透力 Fp (KN·m-1) | 0.198 ± 0.004 | 0.281 ± 0.007 | *** |
| 氨基酸含量 AA (μg·g-1) | 84.13 ± 3.66 | 90.83 ± 2.83 | * |
| 总酚含量 TPh (mg·g-1) | 11.18 ± 0.79 | 14.68 ± 1.08 | ** |
| 单宁含量 TA (mg·g-1) | 33.21 ± 2.26 | 30.79 ± 1.62 | 0.21 |
表3 常绿阔叶林中喜光树种和耐阴树种叶片性状的对比
Table 3 Comparison of leaf traits between light-demanding and shade-tolerant species in an evergreen broad-leaved forest
| 叶片性状 Leaf trait | 喜光树种 Light-demanding species | 耐阴树种 Shadow-tolerant species | p |
|---|---|---|---|
| 叶片植食损伤率 LHDR (%) | 7.13 ± 0.51 | 3.38 ± 0.28 | *** |
| 单位质量碳含量 Cmass (mg·g-1) | 478.19 ± 2.47 | 480.20 ± 3.04 | 0.22 |
| 单位质量氮含量 Nmass (mg·g-1) | 15.71 ± 0.32 | 13.79 ± 0.27 | *** |
| 单位质量磷含量 Pmass (mg·g-1) | 0.864 ± 0.026 | 0.824 ± 0.022 | 0.18 |
| C:N | 31.20 ± 0.67 | 35.79 ± 0.83 | *** |
| C:P | 622.2 ± 24.0 | 637.1 ± 20.7 | 0.54 |
| N:P | 19.70 ± 0.78 | 17.78 ± 0.57 | 0.13 |
| 比叶质量 LMA (g·m-2) | 89.44 ± 3.17 | 96.31 ± 3.36 | 0.06 |
| 叶片撕裂力 Ft (KN·m-1) | 0.299 ± 0.007 | 0.402 ± 0.009 | *** |
| 叶片穿透力 Fp (KN·m-1) | 0.198 ± 0.004 | 0.281 ± 0.007 | *** |
| 氨基酸含量 AA (μg·g-1) | 84.13 ± 3.66 | 90.83 ± 2.83 | * |
| 总酚含量 TPh (mg·g-1) | 11.18 ± 0.79 | 14.68 ± 1.08 | ** |
| 单宁含量 TA (mg·g-1) | 33.21 ± 2.26 | 30.79 ± 1.62 | 0.21 |
图5 叶片植食损伤和叶片性状的主成分(PC)分析。前两个主成分和得分在喜光树种(灰色圆圈)和耐阴树种(绿色圆圈)中以轴表示。叶片性状缩写见表3。
Fig. 5 Principal component (PC) analysis on the leaf herbivory damage and leaf traits. The first two principal components and scores are represented along the axes for light-demanding (gray circle) and shade-tolerant (green circle) species. Abbreviations of leaf traits are provided in Table 3.
附录 叶片植食损伤和叶片性状对前两个主成分的贡献 AA, 氨基酸含量; Cmass, 单位质量碳含量; Fp, 叶片穿透力; Ft, 叶片撕裂力; LHDR, 叶片植食损伤率; LMA, 比叶质量; Nmass, 单位质量氮含量; Pmass, 单位质量磷含量; PC1, 第一主成分; PC2, 第二主成分; TA, 单宁含量; TPh, 总酚含量。
Supplement Contribution of leaf herbivory damage and leaf traits to the first two principal components AA, amino acid content; Cmass, carbon content per unit mass; Fp, leaf force to punch; Ft, leaf force to tear; LHDR, leaf herbivorous damage rate; LMA, leaf mass per area; Nmass, nitrogen content per unit mass; Pmass, phosphorus content per unit mass; PC1, the first principal component; PC2, the second principal component; TA, tannin content; TPh, total phenolic content.
| [1] |
Aldea M, Hamilton JG, Resti JP, Zangerl AR, Berenbaum MR, DeLucia EH (2005). Indirect effects of insect herbivory on leaf gas exchange in soybean. Plant, Cell & Environment, 28, 402-411.
DOI URL |
| [2] |
Björkman C, Berggren Å, Bylund H (2011). Causes behind insect folivory patterns in latitudinal gradients. Journal of Ecology, 99, 367-369.
PMID |
| [3] |
Borer ET, Seabloom EW, Mitchell CE, Cronin JP (2014). Multiple nutrients and herbivores interact to govern diversity, productivity, composition, and infection in a successional grassland. Oikos, 123, 214-224.
DOI URL |
| [4] |
Butler J, Garratt MPD, Leather SR (2012). Fertilisers and insect herbivores: a meta-analysis. Annals of Applied Biology, 161, 223-233.
DOI URL |
| [5] |
Cappelli SL, Pichon NA, Kempel A, Allan E (2020). Sick plants in grassland communities: a growth-defense trade-off is the main driver of fungal pathogen abundance. Ecology Letters, 23, 1349-1359.
DOI PMID |
| [6] | Castagneyrol B, Lagache L, Giffard B, Kremer A, Jactel H (2012). Genetic diversity increases insect herbivory on oak saplings. PLoS ONE, 7, e44247. DOI: 10.1371/journal.pone.0044247. |
| [7] | Cha DH, Appel HM, Frost CJ, Schultz JC, Steiner KC (2010). Red oak responses to nitrogen addition depend on herbivory type, tree family, and site. Forest Ecology and Management, 259, 1930-1937. |
| [8] |
Coley PD, Barone JA (1996). Herbivory and plant defenses in tropical forests. Annual Review of Ecology and Systematics, 27, 305-335.
DOI URL |
| [9] | Condit R, Hernández A, Calderón O, Pérez R, Aguilar S, Comita LS, Hubbell SP, Wright SJ (2025). Lifespan of tropical trees from seed to 1-cm diameter. Forest Ecosystems, 13, 100309. DOI: 10.1016/j.fecs.2025.100309. |
| [10] |
Couture JJ, Meehan TD, Kruger EL, Lindroth RL (2015). Insect herbivory alters impact of atmospheric change on northern temperate forests. Nature Plants, 1, 15016. DOI: 10.1038/nplants.2015.16.
PMID |
| [11] |
DeForest JL, Snell RS (2020). Tree growth response to shifting soil nutrient economy depends on mycorrhizal associations. New Phytologist, 225, 2557-2566.
DOI PMID |
| [12] |
Ebeling A, Strauss AT, Adler PB, Arnillas CA, Barrio IC, Biederman LA, Borer ET, Bugalho MN, Caldeira MC, Cadotte MW, Daleo P, Eisenhauer N, Eskelinen A, Fay PA, Firn J, et al. (2022). Nutrient enrichment increases invertebrate herbivory and pathogen damage in grasslands. Journal of Ecology, 110, 327-339.
DOI URL |
| [13] |
Elser JJ, Urabe J (1999). The stoichiometry of consumer-driven nutrient recycling: theory, observations, and consequences. Ecology, 80, 735-751.
DOI URL |
| [14] | Galmán A, Abdala-Roberts L, Zhang S, Berny-Mier y Teran JC, Rasmann S, Moreira X (2018). A global analysis of elevational gradients in leaf herbivory and its underlying drivers: effects of plant growth form, leaf habit and climatic correlates. Journal of Ecology, 106, 413-421. |
| [15] |
He PC, Wright IJ, Zhu SD, Onoda Y, Liu H, Li RH, Liu XR, Hua L, Oyanoghafo OO, Ye Q (2019). Leaf mechanical strength and photosynthetic capacity vary independently across 57 subtropical forest species with contrasting light requirements. New Phytologist, 223, 607-618.
DOI PMID |
| [16] |
Hidaka A, Kitayama K (2013). Relationship between photosynthetic phosphorus-use efficiency and foliar phosphorus fractions in tropical tree species. Ecology and Evolution, 3, 4872-4880.
DOI PMID |
| [17] | Jia T, Long FQ, Xin HY, Wang XW, Sun T (2025). Leaf herbivory patterns and regulatory factors at 16 forest sites in China. Acta Ecologica Sinica, 45, 4368-4379. |
| [贾婷, 龙福强, 辛浩瑀, 王秀伟, 孙涛 (2025). 中国16个森林站点叶片植食格局及其调控因子. 生态学报, 45, 4368-4379.] | |
| [18] | Jiang J, Wang YP, Liu FC, Du Y, Zhuang W, Chang ZB, Yu MX, Yan JH (2021). Antagonistic and additive interactions dominate the responses of belowground carbon-cycling processes to nitrogen and phosphorus additions. Soil Biology & Biochemistry, 156, 108216. DOI: 10.1016/j.soilbio.2021.108216. |
| [19] |
Jonas JL, Joern A (2008). Host-plant quality alters grass/forb consumption by a mixed-feeding insect herbivore, Melanoplus bivittatus (Orthoptera: Acrididae). Ecological Entomology, 33, 546-554.
DOI URL |
| [20] | Katagiri S, Li CH, Kawaguchi H, Nagayama T (2001). Nutrient return of litterfall in natural evergreen broad-leaved forests in southern China. Resources Science, 23, 58-67. |
| [片桐成夫, 李昌华, 川口英之, 长山泰秀 (2001). 中国南部天然常绿阔叶林的凋落物养分归还. 资源科学, 23, 58-67.] | |
| [21] | Kozlov MV, Lanta V, Zverev V, Zvereva EL (2015). Global patterns in background losses of woody plant foliage to insects. Global Ecology & Biogeography, 24, 1126-1135. |
| [22] |
Kurz WA, Dymond CC, Stinson G, Rampley GJ, Neilson ET, Carroll AL, Ebata T, Safranyik L (2008). Mountain pine beetle and forest carbon feedback to climate change. Nature, 452, 987-990.
DOI |
| [23] |
La Pierre KJ, Smith MD (2016). Soil nutrient additions increase invertebrate herbivore abundances, but not herbivory, across three grassland systems. Oecologia, 180, 485-497.
DOI URL |
| [24] |
Li FR, Dudley TL, Chen BM, Chang XY, Liang LY, Peng SL (2016). Responses of tree and insect herbivores to elevated nitrogen inputs: a meta-analysis. Acta Oecologica, 77, 160-167.
DOI URL |
| [25] |
Liu M, Jiang PX, Chase JM, Liu X (2024). Global insect herbivory and its response to climate change. Current Biology, 34, 2558-2569.
DOI URL |
| [26] |
Loughnan D, Williams JL (2019). Climate and leaf traits, not latitude, explain variation in plant-herbivore interactions across a species’ range. Journal of Ecology, 107, 913-922.
DOI |
| [27] | Lu XK, Mo JM, Zhang W, Mao QG, Liu RZ, Wang C, Wang SH, Zheng MH, Mori T, Mao JH, Zhang YQ, Wang YF, Huang J (2019). Research progress on the effects of simulated atmospheric nitrogen deposition on Chinese forest ecosystems in China: an overview. Journal of Tropical and Subtropical Botany, 27, 500-522. |
| [鲁显楷, 莫江明, 张炜, 毛庆功, 刘荣臻, 王聪, 王森浩, 郑棉海, Mori T, 毛晋花, 张勇群, 王玉芳, 黄娟 (2019). 模拟大气氮沉降对中国森林生态系统影响的研究进展. 热带亚热带植物学报, 27, 500-522.] | |
| [28] |
Machado BB, Orue JPM, Arruda MS, Santos CV, Sarath DS, Goncalves WN, Silva GG, Pistori H, Roel AR, Rodrigues Jr JF (2016). BioLeaf: a professional mobile application to measure foliar damage caused by insect herbivory. Computers and Electronics in Agriculture, 129, 44-55.
DOI URL |
| [29] | Mao QG, Chen H, Wang C, Pang ZQ, Mo JM, Lu XK (2021). Effect of long-term nitrogen and phosphorus additions on understory plant nutrients in a primary tropical forest. Forests, 12, 803. DOI: 10.3390/f12060803. |
| [30] |
Metcalfe DB, Asner GP, Martin RE, Silva Espejo JE, Huasco WH, Farfán Amézquita FF, Carranza-Jimenez L, Galiano Cabrera DF, Baca LD, Sinca F, Huaraca Quispe LP, Taype IA, Mora LE, Dávila AR, Solórzano MM, et al. (2014). Herbivory makes major contributions to ecosystem carbon and nutrient cycling in tropical forests. Ecology Letters, 17, 324-332.
DOI PMID |
| [31] |
Minocha R, Turlapati SA, Long S, McDowell WH, Minocha SC (2015). Long-term trends of changes in pine and oak foliar nitrogen metabolism in response to chronic nitrogen amendments at Harvard Forest, MA. Tree Physiology, 35, 894-909.
DOI PMID |
| [32] | Moles AT, Wallis IR, Foley WJ, Warton DI, Stegen JC, Bisigato AJ, Cella-Pizarro L, Clark CJ, Cohen PS, Cornwell WK, Edwards W, Ejrnæs R, Gonzales-Ojeda T, Graae BJ, Hay G, et al. (2011). Putting plant resistance traits on the map: a test of the idea that plants are better defended at lower latitudes. New Phytologist, 191, 777-788. |
| [33] |
Moore TR, Trofymow JA, Prescott CE, Titus BD,CIDET Working Group (2011). Nature and nurture in the dynamics of C, N and P during litter decomposition in Canadian forests. Plant and Soil, 339, 163-175.
DOI URL |
| [34] |
Mueller UG, Gerardo NM, Aanen DK, Six DL, Schultz TR (2005). The evolution of agriculture in insects. Annual Review of Ecology, Evolution, and Systematics, 36, 563-595.
DOI URL |
| [35] |
Nebel G, Dragsted J, Vega AS (2001). Litter fall, biomass and net primary production in flood plain forests in the Peruvian Amazon. Forest Ecology and Management, 150, 93-102.
DOI URL |
| [36] |
Onoda Y, Westoby M, Adler PB, Choong AMF, Clissold FJ, Cornelissen JHC, Díaz S, Dominy NJ, Elgart A, Enrico L, Fine PVA, Howard JJ, Jalili A, Kitajima K, Kurokawa H, et al. (2011). Global patterns of leaf mechanical properties. Ecology Letters, 14, 301-312.
DOI PMID |
| [37] |
Peng YF, Peng ZP, Zeng XT, Houx JH (2019). Effects of nitrogen-phosphorus imbalance on plant biomass production: a global perspective. Plant and Soil, 436, 245-252.
DOI |
| [38] |
Rheubottom SI, Barrio IC, Kozlov MV, Alatalo JM, Andersson T, Asmus AL, Baubin C, Brearley FQ, Egelkraut DD, Ehrich D, Gauthier G, Jónsdóttir IS, Konieczka S, Lévesque E, Olofsson J, et al. (2019). Hiding in the background: community-level patterns in invertebrate herbivory across the tundra biome. Polar Biology, 42, 1881-1897.
DOI |
| [39] |
Ritchie ME, Tilman D, Knops JMH (1998). Herbivore effects on plant and nitrogen dynamics in oak savanna. Ecology, 79, 165-177.
DOI URL |
| [40] |
Sam K, Koane B, Sam L, Mrazova A, Segar S, Volf M, Moos M, Simek P, Sisol M, Novotny V (2020). Insect herbivory and herbivores of Ficus species along a rain forest elevational gradient in Papua New Guinea. Biotropica, 52, 263-276.
DOI URL |
| [41] | Song LN, Fan XD, Ji YS, Gu YJ, Li L (2010). Relationship betweem feeding rate, loss rate and tannins content in Castanopsis sclerophylla leaves under different habit. Journal of Anhui Agricultural Sciences, 38, 3784-3786. |
| [宋丽娜, 范旭东, 冀永生, 顾咏洁, 李伶 (2010). 不同生境中苦槠叶片取食率损失率及单宁含量变化关系. 安徽农业科学, 38, 3784-3786.] | |
| [42] |
Staudacher K, Schallhart N, Thalinger B, Wallinger C, Juen A, Traugott M (2013). Plant diversity affects behavior of generalist root herbivores, reduces crop damage, and enhances crop yield. Ecological Applications, 23, 1135-1145.
PMID |
| [43] | Throop HL, Lerdau MT (2004). Effects of nitrogen deposition on insect herbivory: implications for community and ecosystem processes. Ecosystems, 7, 109-133. |
| [44] | Turcotte MM, Davies TJ, Thomsen CJM, Johnson MTJ (2014). Macroecological and macroevolutionary patterns of leaf herbivory across vascular plants. Proceedings of the Royal Society B: Biological Sciences, 281, 20140555. DOI: 10.1098/rspb.2014.0555. |
| [45] |
Wright SJ, Yavitt JB, Wurzburger N, Turner BL, Tanner EVJ, Sayer EJ, Santiago LS, Kaspari M, Hedin LO, Harms KE, Garcia MN, Corre MD (2011). Potassium, phosphorus, or nitrogen limit root allocation, tree growth, or litter production in a lowland tropical forest. Ecology, 92, 1616-1625.
PMID |
| [46] |
Yavitt JB, Harms KE, Garcia MN, Mirabello MJ, Wright SJ (2011). Soil fertility and fine root dynamics in response to 4 years of nutrient (N, P, K) fertilization in a lowland tropical moist forest, Panama. Austral Ecology, 36, 433-445.
DOI URL |
| [47] | Ye XM, Bu WS, Hu XF, Wang FC, Sun RX, He PC, Liang XY, Chen FS (2023). Are small trees more responsive to nutrient addition than large trees in an evergreen broadleaved forest. Forest Ecology and Management, 543, 121129. DOI: 10.1016/j.foreco.2023.121129. |
| [48] |
Zhao CT, Xia QL, Tian D, Chen BR, Zhu RD, Liu XH, Yu G, Ji CJ (2024). Effects of long-term nitrogen addition on leaf secondary metabolites of the dominant plant species in a temperate deciduous broad-leaved forest. Chinese Journal of Plant Ecology, 48, 1576-1588.
DOI URL |
|
[赵常提, 夏青霖, 田地, 陈冰瑞, 朱瑞德, 刘宵含, 俞果, 吉成均 (2024). 长期氮添加对温带落叶阔叶林优势植物叶片次生代谢产物的影响. 植物生态学报, 48, 1576-1588.]
DOI |
|
| [49] | Zvereva EL, Castagneyrol B, Kozlov MV (2024). Does spatial variation in insect herbivory match variations in plant quality? A meta-analysis. Ecology Letters, 27, e14440. DOI: 10.1111/ele.14440. |
| [50] |
Zvereva EL, Kozlov MV (2012). Sources of variation in plant responses to belowground insect herbivory: a meta-analysis. Oecologia, 169, 441-452.
DOI PMID |
| [51] |
Zvereva EL, Kozlov MV (2014). Effects of herbivory on leaf life span in woody plants: a meta-analysis. Journal of Ecology, 102, 873-881.
DOI URL |
| [1] | 卢玉鹏, 许纪元, 张晓曦, 王博雅, 谢博, 刘增文. 林下药用植物淋出物对红桦和杜仲枯落物分解及土壤酶活性的影响[J]. 植物生态学报, 2017, 41(6): 639-649. |
| 阅读次数 | ||||||
|
全文 |
|
|||||
|
摘要 |
|
|||||
Copyright © 2026 版权所有 《植物生态学报》编辑部
地址: 北京香山南辛村20号, 邮编: 100093
Tel.: 010-62836134, 62836138; Fax: 010-82599431; E-mail: apes@ibcas.ac.cn, cjpe@ibcas.ac.cn
备案号: 京ICP备16067583号-19