Chin J Plant Ecol ›› 2025, Vol. 49 ›› Issue (2): 356-366.DOI: 10.17521/cjpe.2024.0042 cstr: 32100.14.cjpe.2024.0042
• Research Articles • Previous Articles
CHEN Wen-Yi1,2, WANG Zhi-Yong1,2, ZHOU Meng-Yan1, MA Wen-Jun1, WANG Jun-Hui1, LUO Zhi-Bin1,3,4, ZHOU Jing1,*()
Received:
2024-02-07
Accepted:
2024-08-23
Online:
2025-02-20
Published:
2025-02-20
Contact:
ZHOU Jing
Supported by:
CHEN Wen-Yi, WANG Zhi-Yong, ZHOU Meng-Yan, MA Wen-Jun, WANG Jun-Hui, LUO Zhi-Bin, ZHOU Jing. Biomass allocation and allometric growth model of young Catalpa bungei[J]. Chin J Plant Ecol, 2025, 49(2): 356-366.
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URL: https://www.plant-ecology.com/EN/10.17521/cjpe.2024.0042
样地 Sample site | 株数 Number of plants | 胸径 D (cm) | 年龄 Age (a) | 造林密度 Afforestation density (ind.·hm-2) | 年降水量 Mean annual precipitation (mm) | 年平均气温 Mean annual air temperature (℃) | 土壤类型 Soil type | ||||
---|---|---|---|---|---|---|---|---|---|---|---|
0-5 | 5-10 | 10-15 | 15-20 | 20-25 | |||||||
山东菏泽 Heze, Shandong | 9 | 1 | 2 | 2 | 3 | 1 | 5 | 833 | 782.6 ± 69.5 | 15.58 ± 0.05 | 冲积土 Fluvisol |
河南永城 Yongcheng, Henan | 8 | 1 | 2 | 3 | 2 | 0 | 4 | 833 | 888.1 ± 72.6 | 16.67 ± 0.11 | 冲积土 Fluvisol |
湖北襄阳 Xiangyang, Hubei | 12 | 1 | 3 | 3 | 2 | 3 | 5 | 833 | 908.6 ± 100.4 | 16.40 ± 0.09 | 始成土 Inceptisol |
湖北石首 Shishou, Hubei | 12 | 2 | 2 | 3 | 2 | 3 | 3, 8 | 833 | 1 222.8 ± 77.8 | 17.77 ± 0.13 | 淋溶土 Alfisol |
总计 Total | 41 | 5 | 9 | 11 | 9 | 7 | - | - | - | - | - |
建模组 Modeling group | 28 | 3 | 7 | 7 | 6 | 5 | - | - | - | - | - |
验证组 Testing group | 13 | 2 | 2 | 4 | 3 | 2 | - | - | - | - | - |
Table 1 Sample size of Catalpa bungei with different D grades and environmental conditions of the sample sites
样地 Sample site | 株数 Number of plants | 胸径 D (cm) | 年龄 Age (a) | 造林密度 Afforestation density (ind.·hm-2) | 年降水量 Mean annual precipitation (mm) | 年平均气温 Mean annual air temperature (℃) | 土壤类型 Soil type | ||||
---|---|---|---|---|---|---|---|---|---|---|---|
0-5 | 5-10 | 10-15 | 15-20 | 20-25 | |||||||
山东菏泽 Heze, Shandong | 9 | 1 | 2 | 2 | 3 | 1 | 5 | 833 | 782.6 ± 69.5 | 15.58 ± 0.05 | 冲积土 Fluvisol |
河南永城 Yongcheng, Henan | 8 | 1 | 2 | 3 | 2 | 0 | 4 | 833 | 888.1 ± 72.6 | 16.67 ± 0.11 | 冲积土 Fluvisol |
湖北襄阳 Xiangyang, Hubei | 12 | 1 | 3 | 3 | 2 | 3 | 5 | 833 | 908.6 ± 100.4 | 16.40 ± 0.09 | 始成土 Inceptisol |
湖北石首 Shishou, Hubei | 12 | 2 | 2 | 3 | 2 | 3 | 3, 8 | 833 | 1 222.8 ± 77.8 | 17.77 ± 0.13 | 淋溶土 Alfisol |
总计 Total | 41 | 5 | 9 | 11 | 9 | 7 | - | - | - | - | - |
建模组 Modeling group | 28 | 3 | 7 | 7 | 6 | 5 | - | - | - | - | - |
验证组 Testing group | 13 | 2 | 2 | 4 | 3 | 2 | - | - | - | - | - |
胸径 D (cm) | 主干 Trunk (kg·plant-1) | 枝条 Branch (kg·plant-1) | 叶 Leaf (kg·plant-1) | 粗根 Coarse root (kg·plant-1) | 细根 Fine root (kg·plant-1) | |||||
---|---|---|---|---|---|---|---|---|---|---|
范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | |
0-5 | 0.83-6.56 | 2.52Ad | 0.15-5.46 | 1.55ABc | 0.11-0.55 | 0.27Bd | 0.51-3.21 | 1.39ABd | 0.01-0.04 | 0.02Bc |
5-10 | 3.47-17.30 | 8.35Ad | 1.12-6.15 | 3.23Bc | 0.28-3.41 | 1.30BCcd | 1.63-10.95 | 3.71Bcd | 0.01-0.07 | 0.05Cc |
10-15 | 14.45-37.18 | 26.49Ac | 7.33-20.09 | 13.04Bc | 1.29-6.92 | 4.06Dbc | 4.75-14.74 | 8.60Cc | 0.04-0.15 | 0.11Ec |
15-20 | 41.87-73.16 | 55.63Ab | 16.95-76.11 | 32.92Bb | 1.79-16.09 | 7.21CDab | 8.40-25.44 | 16.52Cb | 0.10-0.27 | 0.19Db |
20-25 | 53.91-116.49 | 89.22Aa | 35.50-73.64 | 56.43Ba | 2.87-19.19 | 9.61Da | 19.78-42.27 | 31.02Ca | 0.13-0.56 | 0.30Da |
Table 2 Biomass of trunk, branch, leaf, coarse root and fine root of different diameter classes of Catalpa bungei
胸径 D (cm) | 主干 Trunk (kg·plant-1) | 枝条 Branch (kg·plant-1) | 叶 Leaf (kg·plant-1) | 粗根 Coarse root (kg·plant-1) | 细根 Fine root (kg·plant-1) | |||||
---|---|---|---|---|---|---|---|---|---|---|
范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | |
0-5 | 0.83-6.56 | 2.52Ad | 0.15-5.46 | 1.55ABc | 0.11-0.55 | 0.27Bd | 0.51-3.21 | 1.39ABd | 0.01-0.04 | 0.02Bc |
5-10 | 3.47-17.30 | 8.35Ad | 1.12-6.15 | 3.23Bc | 0.28-3.41 | 1.30BCcd | 1.63-10.95 | 3.71Bcd | 0.01-0.07 | 0.05Cc |
10-15 | 14.45-37.18 | 26.49Ac | 7.33-20.09 | 13.04Bc | 1.29-6.92 | 4.06Dbc | 4.75-14.74 | 8.60Cc | 0.04-0.15 | 0.11Ec |
15-20 | 41.87-73.16 | 55.63Ab | 16.95-76.11 | 32.92Bb | 1.79-16.09 | 7.21CDab | 8.40-25.44 | 16.52Cb | 0.10-0.27 | 0.19Db |
20-25 | 53.91-116.49 | 89.22Aa | 35.50-73.64 | 56.43Ba | 2.87-19.19 | 9.61Da | 19.78-42.27 | 31.02Ca | 0.13-0.56 | 0.30Da |
胸径 D (cm) | 整株 Total tree (kg·plant -1) | 地上 Aboveground (kg·plant -1) | 地下 Belowground (kg·plant-1) | 根冠比 Root to shoot ratio | ||||
---|---|---|---|---|---|---|---|---|
范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | |
0-5 | 1.69-15.79 | 5.76 | 1.17-12.57 | 4.34 | 0.52-3.22 | 1.42 | 0.26-0.64 | 0.42a |
5-10 | 7.61-34.82 | 16.63 | 4.87-23.82 | 12.87 | 1.63-11.00 | 3.76 | 0.15-0.56 | 0.32a |
10-15 | 35.13-68.06 | 52.29 | 28.74-55.48 | 43.58 | 4.79-14.90 | 8.71 | 0.14-0.28 | 0.20b |
15-20 | 77.64-180.77 | 112.47 | 62.55-111.58 | 95.76 | 8.63-25.68 | 16.71 | 0.08-0.24 | 0.18b |
20-25 | 129.19-248.95 | 186.59 | 101.02-209.32 | 155.27 | 20.08-42.40 | 31.32 | 0.15-0.28 | 0.20b |
Table 3 Biomass of total tree, above- and below-ground parts of different diameter classes of Catalpa bungei
胸径 D (cm) | 整株 Total tree (kg·plant -1) | 地上 Aboveground (kg·plant -1) | 地下 Belowground (kg·plant-1) | 根冠比 Root to shoot ratio | ||||
---|---|---|---|---|---|---|---|---|
范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | 范围 Range | 平均值 Mean | |
0-5 | 1.69-15.79 | 5.76 | 1.17-12.57 | 4.34 | 0.52-3.22 | 1.42 | 0.26-0.64 | 0.42a |
5-10 | 7.61-34.82 | 16.63 | 4.87-23.82 | 12.87 | 1.63-11.00 | 3.76 | 0.15-0.56 | 0.32a |
10-15 | 35.13-68.06 | 52.29 | 28.74-55.48 | 43.58 | 4.79-14.90 | 8.71 | 0.14-0.28 | 0.20b |
15-20 | 77.64-180.77 | 112.47 | 62.55-111.58 | 95.76 | 8.63-25.68 | 16.71 | 0.08-0.24 | 0.18b |
20-25 | 129.19-248.95 | 186.59 | 101.02-209.32 | 155.27 | 20.08-42.40 | 31.32 | 0.15-0.28 | 0.20b |
组分生物量 Component biomass | 降水量 Precipitation | 气温 Air temperature | 年龄 Age |
---|---|---|---|
整株 Total tree | -0.029 | -0.110 | 0.496** |
地上部分 Aboveground | -0.054 | -0.129 | 0.487** |
地下部分 Belowground | 0.043 | -0.071 | 0.566** |
主干 Trunk | -0.015 | -0.115 | 0.507** |
枝条 Branch | -0.085 | -0.126 | 0.427** |
叶 Leaf | -0.215 | -0.157 | 0.141 |
粗根 Coarse root | 0.048 | -0.066 | 0.562** |
细根 Fine root | 0.054 | -0.110 | 0.481** |
Table 4 Correlation coefficient between component biomass of Catalpa bungei., precipitation, air temperature and the tree age
组分生物量 Component biomass | 降水量 Precipitation | 气温 Air temperature | 年龄 Age |
---|---|---|---|
整株 Total tree | -0.029 | -0.110 | 0.496** |
地上部分 Aboveground | -0.054 | -0.129 | 0.487** |
地下部分 Belowground | 0.043 | -0.071 | 0.566** |
主干 Trunk | -0.015 | -0.115 | 0.507** |
枝条 Branch | -0.085 | -0.126 | 0.427** |
叶 Leaf | -0.215 | -0.157 | 0.141 |
粗根 Coarse root | 0.048 | -0.066 | 0.562** |
细根 Fine root | 0.054 | -0.110 | 0.481** |
组分生物量 Component biomass | 回归模型 Regression model | a | b | R2 | RMSE | AICc |
---|---|---|---|---|---|---|
主干 Trunk | ln W = a + bln D | -2.521 | 2.257 | 0.949 3 | 0.296 8 | -62.04 |
ln W = a + b ln H | -3.978 | 3.400 | 0.748 9 | 0.660 2 | -17.27 | |
ln W = a + b ln (D2H) | -3.123 | 0.881 | 0.935 2 | 0.335 3 | -55.21 | |
枝条 Branch | ln W = a + bln D | -4.439 | 2.716 | 0.902 7 | 0.507 4 | -32.01 |
ln W = a + b ln H | -5.898 | 3.948 | 0.663 0 | 0.944 1 | 2.76 | |
ln W = a + bln (D2H) | -5.113 | 1.053 | 0.876 9 | 0.570 6 | -25.44 | |
叶 Leaf | ln W = a + bln D | -4.502 | 2.203 | 0.839 2 | 0.548 6 | -27.64 |
ln W = a + bln H | -5.761 | 3.239 | 0.630 6 | 0.831 5 | -4.35 | |
ln W = a + bln (D2H) | -5.061 | 0.856 | 0.818 8 | 0.582 4 | -24.29 | |
粗根 Coarse root | ln W = a + bln D | -2.629 | 1.894 | 0.903 0 | 0.353 2 | -52.30 |
ln W = a + bln H | -3.895 | 2.875 | 0.722 8 | 0.597 2 | -22.89 | |
ln W = a + bln (D2H) | -3.146 | 0.741 | 0.893 6 | 0.369 9 | -49.72 | |
细根 Fine root | ln W = a + bln D | -6.298 | 1.565 | 0.777 4 | 0.476 6 | -35.52 |
ln W = a + bln H | -7.786 | 2.591 | 0.740 3 | 0.514 8 | -31.21 | |
ln W = a + bln (D2H) | -6.805 | 0.624 | 0.798 4 | 0.453 5 | -38.30 | |
整株 Total tree | ln W = a + bln D | -1.836 | 2.264 | 0.946 0 | 0.307 8 | -60.00 |
ln W = a + bln H | -3.203 | 3.364 | 0.726 3 | 0.692 7 | -14.58 | |
ln W = a + bln (D2H) | -2.424 | 0.882 | 0.927 1 | 0.357 5 | -51.62 | |
地上 Aboveground | ln W = a + bln D | -2.313 | 2.368 | 0.943 6 | 0.329 2 | -56.23 |
ln W = a + bln H | -3.715 | 3.505 | 0.718 8 | 0.735 2 | -11.24 | |
ln W = a + bln (D2H) | -2.923 | 0.921 | 0.923 1 | 0.384 4 | -47.56 | |
地下 Belowground | ln W = a + bln D | -2.602 | 1.889 | 0.903 8 | 0.350 6 | -52.70 |
ln W = a + bln H | -3.863 | 2.866 | 0.723 4 | 0.594 5 | -23.14 | |
ln W = a + bln (D2H) | -3.117 | 0.739 | 0.894 4 | 0.367 3 | -50.11 |
Table 5 Allometric growth models of whole Catalpa bungei and each component
组分生物量 Component biomass | 回归模型 Regression model | a | b | R2 | RMSE | AICc |
---|---|---|---|---|---|---|
主干 Trunk | ln W = a + bln D | -2.521 | 2.257 | 0.949 3 | 0.296 8 | -62.04 |
ln W = a + b ln H | -3.978 | 3.400 | 0.748 9 | 0.660 2 | -17.27 | |
ln W = a + b ln (D2H) | -3.123 | 0.881 | 0.935 2 | 0.335 3 | -55.21 | |
枝条 Branch | ln W = a + bln D | -4.439 | 2.716 | 0.902 7 | 0.507 4 | -32.01 |
ln W = a + b ln H | -5.898 | 3.948 | 0.663 0 | 0.944 1 | 2.76 | |
ln W = a + bln (D2H) | -5.113 | 1.053 | 0.876 9 | 0.570 6 | -25.44 | |
叶 Leaf | ln W = a + bln D | -4.502 | 2.203 | 0.839 2 | 0.548 6 | -27.64 |
ln W = a + bln H | -5.761 | 3.239 | 0.630 6 | 0.831 5 | -4.35 | |
ln W = a + bln (D2H) | -5.061 | 0.856 | 0.818 8 | 0.582 4 | -24.29 | |
粗根 Coarse root | ln W = a + bln D | -2.629 | 1.894 | 0.903 0 | 0.353 2 | -52.30 |
ln W = a + bln H | -3.895 | 2.875 | 0.722 8 | 0.597 2 | -22.89 | |
ln W = a + bln (D2H) | -3.146 | 0.741 | 0.893 6 | 0.369 9 | -49.72 | |
细根 Fine root | ln W = a + bln D | -6.298 | 1.565 | 0.777 4 | 0.476 6 | -35.52 |
ln W = a + bln H | -7.786 | 2.591 | 0.740 3 | 0.514 8 | -31.21 | |
ln W = a + bln (D2H) | -6.805 | 0.624 | 0.798 4 | 0.453 5 | -38.30 | |
整株 Total tree | ln W = a + bln D | -1.836 | 2.264 | 0.946 0 | 0.307 8 | -60.00 |
ln W = a + bln H | -3.203 | 3.364 | 0.726 3 | 0.692 7 | -14.58 | |
ln W = a + bln (D2H) | -2.424 | 0.882 | 0.927 1 | 0.357 5 | -51.62 | |
地上 Aboveground | ln W = a + bln D | -2.313 | 2.368 | 0.943 6 | 0.329 2 | -56.23 |
ln W = a + bln H | -3.715 | 3.505 | 0.718 8 | 0.735 2 | -11.24 | |
ln W = a + bln (D2H) | -2.923 | 0.921 | 0.923 1 | 0.384 4 | -47.56 | |
地下 Belowground | ln W = a + bln D | -2.602 | 1.889 | 0.903 8 | 0.350 6 | -52.70 |
ln W = a + bln H | -3.863 | 2.866 | 0.723 4 | 0.594 5 | -23.14 | |
ln W = a + bln (D2H) | -3.117 | 0.739 | 0.894 4 | 0.367 3 | -50.11 |
Fig. 4 Relationships between the biomass observed and predicted by the optimal growth models. The solid line in the figure is the result of linear fitting between the predicted value and the observed value; slope, the slope of the fitted line. The black dashed line indicates a 1:1 relationship. MAPE, mean absolute percentage error.
[1] | Ammer C, Wagner S (2005). An approach for modelling the mean fine-root biomass of Norway spruce stands. Trees, 19, 145-153. |
[2] | Aneseyee AB, Soromessa T, Elias E, Feyisa GL (2021). Allometric equations for selected Acacia species (Vachellia and Senegalia genera) of Ethiopia. Carbon Balance and Management, 16, 34. DOI: 10.1186/s13021-021-00196-1. |
[3] |
Bowman DMJS, Brienen RJW, Gloor E, Phillips OL, Prior LD (2013). Detecting trends in tree growth: not so simple. Trends in Plant Science, 18, 11-17.
DOI PMID |
[4] | Chang L, Liu K, Wang LG, Yang XL, Sun H (2022). First report of Phytophthora nicotianae causing stem canker of Catalpa bungei (Chinese Catalpa) in China. Plant Disease, 106, 1309. DOI: 10.1094/PDIS-08-21-1778-PDN. |
[5] | Chen C, Ko SH, Lam TY (2021). Modeling biomass allocation strategy of young planted Zelkova serrata trees in Taiwan with component ratio method and seemingly unrelated regressions. Scientific Reports, 11, 7536. DOI: 10.1038/ s41598-021-87129-7. |
[6] | Chen JL, Fang X, Wu AC, Xiang WH, Lei PF, Ouyang S (2024). Allometric equations for estimating biomass of natural shrubs and young trees of subtropical forests. New Forests, 55, 15-46. |
[7] | Chen Q (2015). Modeling aboveground tree woody biomass using national-scale allometric methods and airborne lidar. ISPRS Journal of Photogrammetry and Remote Sensing, 106, 95-106. |
[8] | Chen W, Zhang Q, Cihlar J, Bauhus J, Price DT (2004). Estimating fine-root biomass and production of boreal and cool temperate forests using aboveground measurements: a new approach. Plant and Soil, 265, 31-46. |
[9] | Chen XY, Wang YJ, Li HW, Zhai BQ, Chang J, Wei HM (2021). Preliminary report of demonstration forest test of improved seed of Catalpa bungei. Journal of Henan Forestry Science and Technology, 41(3), 19-21. |
[陈晓燕, 王燕军, 李红伟, 翟宝黔, 常娟, 魏洪敏 (2021). 楸树良种示范林试验初报. 河南林业科技, 41(3), 19-21.] | |
[10] | Chojnacky DC, Heath LS, Jenkins JC (2014). Updated generalized biomass equations for North American tree species. Forestry, 87, 129-151. |
[11] | Dong LH, Zhang LJ, Li FR (2015). Developing additive systems of biomass equations for nine hardwood species in Northeast China. Trees, 29, 1149-1163. |
[12] |
Dybzinski R, Farrior C, Wolf A, Reich PB, Pacala SW (2011). Evolutionarily stable strategy carbon allocation to foliage, wood, and fine roots in trees competing for light and nitrogen: an analytically tractable, individual-based model and quantitative comparisons to data. The American Naturalist, 177, 153-166.
DOI PMID |
[13] | Guan ZZ, Lin D, Chen D, Guo Y, Lu Y, Han Q, Li N, Su Y, Li J, Wang J, Ma W, Qiu Q, He Q (2022). Soil microbial communities response to different fertilization regimes in young Catalpa bungei plantation. Frontiers in Microbiology, 13, 948875. DOI: 10.3389/fmicb.2022.948875. |
[14] | Han WX, Fang JY (2008). Review on the mechanism models of allometric scaling laws: 3/4 vs. 2/3 power. Chinese Journal of Plant Ecology, 32, 951-960. |
[韩文轩, 方精云 (2008). 幂指数异速生长机制模型综述. 植物生态学报, 32, 951-960.]
DOI |
|
[15] | Holland R, Castro G, Chavana-Bryant C, Levy R, Moat J, Robson T, Wilkinson T, Wilkes P, Yang WX, Disney M (2024). Giant sequoia (Sequoiadendron giganteum) in the UK: carbon storage potential and growth rates. Royal Society Open Science, 11, 230603. DOI: 10.1098/rsos.230603. |
[16] | Hossain M, Saha C, Abdullah SMR, Saha S, Siddique MRH (2016). Allometric biomass, nutrient and carbon stock models for Kandelia candel of the Sundarbans, Bangladesh. Trees, 30, 709-717. |
[17] | Inagaki Y, Nakanishi A, Tange T (2020). A simple method for leaf and branch biomass estimation in Japanese cedar plantations. Trees, 34, 349-356. |
[18] |
Ishihara MI, Utsugi H, Tanouchi H, Aiba M, Kurokawa H, Onoda Y, Nagano M, Umehara T, Ando M, Miyata R, Hiura T (2015). Efficacy of generic allometric equations for estimating biomass: a test in Japanese natural forests. Ecological Applications, 25, 1433-1446.
PMID |
[19] | Jara MC, Henry M, Réjou-Méchain M, Wayson C, Zapata-Cuartas M, Piotto D, Guier FA, Lombis HC, López EC, Lara RC, Rojas KC, Pasquel JD, Montoya AD, Vega JF, Galo AJ, et al. (2015). Guidelines for documenting and reporting tree allometric equations. Annals of Forest Science, 72, 763-768. |
[20] |
Jucker T, Caspersen J, Chave J, Antin C, Barbier N, Bongers F, Dalponte M, van Ewijk KY, Forrester DI, Haeni M, Higgins SI, Holdaway RJ, Iida Y, Lorimer C, Marshall PL, et al. (2017). Allometric equations for integrating remote sensing imagery into forest monitoring programmes. Global Change Biology, 23, 177-190.
DOI PMID |
[21] | Kachamba DJ, Eid T, Gobakken T (2016). Above- and belowground biomass models for trees in the miombo woodlands of Malawi. Forests, 7, 38. DOI: 10.3390/f7020038. |
[22] | Kaushal R, Islam S, Tewari S, Tomar JMS, Thapliyal S, Madhu M, Trinh TL, Singh T, Singh A, Durai J (2022). An allometric model-based approach for estimating biomass in seven Indian bamboo species in western Himalayan foothills, India. Scientific Reports, 12, 7527. DOI: 10.1038/s41598-022-11394-3. |
[23] | Konôpka B, Murgaš V, Pajtík J, Šebeň V, Barka I (2023). Tree biomass and leaf area allometric relations for Betula pendula Roth based on samplings in the western carpathians. Plants, 12, 1607. DOI: 10.3390/plants12081607. |
[24] | Li C, Barclay H, Roitberg B, Lalonde R (2020). Forest productivity enhancement and compensatory growth: a review and synthesis. Frontiers in Plant Science, 11, 575211. DOI: 10.3389/fpls.2020.575211. |
[25] | Li W (2014). Biomass Allocation Patterns and Allometric Models of Larix gmelinii. Master degree dissertation, Northeast Forestry University, Harbin. 2-45. |
[李巍 (2014). 兴安落叶松生物量分配格局和异速生长模型. 硕士学位论文, 东北林业大学, 哈尔滨. 2-45.] | |
[26] | Lin KM, Lyu MK, Jiang MH, Chen YM, Li YQ, Chen GS, Xie JS, Yang YS (2017). Improved allometric equations for estimating biomass of the three Castanopsis carlesii H. forest types in subtropical China. New Forests, 48, 115-135. |
[27] | Lister AJ, Andersen H, Frescino T, Gatziolis D, Healey S, Heath LS, Liknes GC, McRoberts R, Moisen GG, Nelson M, Riemann R, Schleeweis K, Schroeder TA, Westfall J, Wilson BT (2020). Use of remote sensing data to improve the efficiency of national forest inventories: a case study from the United States national forest inventory. Forests, 11, 1364. DOI: 10.3390/f11121364. |
[28] | Ma WJ, Yi F, Xiao Y, Yang GJ, Chen FJ, Wang JH (2020). Isolation of leaf mesophyll protoplasts optimized by orthogonal design for transient gene expression in Catalpa bungei. Scientia Horticulturae, 274, 109684. DOI: 10.1016/j.scienta.2020.109684. |
[29] | Meng SW, Zhou G, Liu WH, Yu J, Zhou H, Liu QJ (2024). Species-specific and generalized allometric equations for improving aboveground biomass estimations of 33 understory woody species in northeastern China forest ecosystems. Canadian Journal of Forest Research, 54, 524-542. |
[30] | Mensah S, Kakaï RG, Seifert T (2016). Patterns of biomass allocation between foliage and woody structure: the effects of tree size and specific functional traits. Annals of Forest Research, 59, 49-60. |
[31] | Moussa M, Mahamane L (2018). Allometric models for estimating aboveground biomass and carbon in Faidherbia albida and Prosopis africana under agroforestry parklands in drylands of Niger. Journal of Forestry Research, 29, 1703-1717. |
[32] | Pan Y, Birdsey RA, Phillips OL, Jackson RB (2013). The structure, distribution, and biomass of the world’s forests. Annual Review of Ecology, Evolution, and Systematics, 44, 593-622. |
[33] |
Paul KI, Roxburgh SH, Chave J, England JR, Zerihun A, Specht A, Lewis T, Bennett LT, Baker TG, Adams MA, Huxtable D, Montagu KD, Falster DS, Feller M, Sochacki S, et al. (2016). Testing the generality of above-ground biomass allometry across plant functional types at the continent scale. Global Change Biology, 22, 2106-2124.
DOI PMID |
[34] | Peichl M, Arain MA (2007). Allometry and partitioning of above- and belowground tree biomass in an age-sequence of white pine forests. Forest Ecology and Management, 253, 68-80. |
[35] |
Poorter H, Jagodzinski AM, Ruiz-Peinado R, Kuyah S, Luo YJ, Oleksyn J, Usoltsev VA, Buckley TN, Reich PB, Sack L (2015). How does biomass distribution change with size and differ among species? An analysis for 1200 plant species from five continents. New Phytologist, 208, 736-749.
DOI PMID |
[36] | Qiu FY, Xiao FM, Wu YF, He XS (2019). Growth and biomass distribution of the middle-age and young Phoebe bournei. Hubei Foresty Science and Technology, 48(3), 12-15. |
[邱凤英, 肖复明, 伍艳芳, 何小三 (2019). 中幼龄闽楠生长及生物量分配特征研究. 湖北林业科技, 48(3), 12-15.] | |
[37] | Quan JE, Ni RY, Wang YG, Sun JJ, Ma MY, Bi HT (2022). Effects of different growth regulators on the rooting of Catalpa bignonioides softwood cuttings. Life, 12, 1231. DOI: 10.3390/life12081231. |
[38] | Roxburgh SH, Paul KI, Clifford D, England JR, Raison RJ (2015). Guidelines for constructing allometric models for the prediction of woody biomass: How many individuals to harvest? Ecosphere, 6, 1-27. |
[39] | Schindler Z, Seifert T, Sheppard JP, Morhart C (2023). Allometric models for above-ground biomass, carbon and nutrient content of wild cherry (Prunus avium L.) trees in agroforestry systems. Annals of Forest Science, 80, 28. DOI: 10.1186/s13595-023-01196-6. |
[40] | Shahabedini S, Ghahramany L, Pulido F, Khosravi S, Moreno G (2018). Estimating leaf biomass of pollarded lebanon oak in open silvopastoral systems using allometric equations. Trees, 32, 99-108. |
[41] | Solomon N, Birhane E, Tadesse T, Treydte AC, Meles K (2017). Carbon stocks and sequestration potential of dry forests under community management in Tigray, Ethiopia. Ecological Processes, 6, 20. DOI: 10.1186/s13717-017-0088-2. |
[42] |
Strand AE, Pritchard SG, McCormack ML, Davis MA, Oren R (2008). Irreconcilable differences: fine-root life spans and soil carbon persistence. Science, 319, 456-458.
DOI PMID |
[43] | Sun TT, Ren RH, Xing MM, Duan QX, Zhao L, Yan WW, Fang Y, Zhang SY, Dong H, Wang MR, Heng QM, Chen WY, Xu T, Kou LL, Li KP, et al. (2024). Morphological and physiological plasticity of Catalpa bungei roots under partial root-zone drought as affected by nitrogen forms. New Forests, 55, 383-402. |
[44] | Tobin B, Black K, Osborne B, Reidy B, Bolger T, Nieuwenhuis M (2006). Assessment of allometric algorithms for estimating leaf biomass, leaf area index and litter fall in different-aged Sitka spruce forests. Forestry, 79, 453-465. |
[45] | Wang CK (2006). Biomass allometric equations for 10 co-occurring tree species in Chinese temperate forests. Forest Ecology and Management, 222, 9-16. |
[46] | Wang JC, Qin XM, Xu SQ, Zhao MY, Shu PQ, Xu FJ, Ma JY, Sun Y, Dong H, Guo ZY, Long DP, Ma WJ, Lu YZ, Xie XM, Chen YL, Chu J, Wang JH, Zhang Y (2021). Nitrogen availability affects stem development and response to differential root-zone drought stress in Catalpa bungei. Environmental and Experimental Botany, 186, 104429. DOI: 10.1016/j.envexpbot.2021.104429. |
[47] | Xiang WH, Liu SH, Deng XW, Shen AH, Lei XD, Tian DL, Zhao MF, Peng CH (2011). General allometric equations and biomass allocation of Pinus massoniana trees on a regional scale in southern China. Ecological Research, 26, 697-711. |
[48] | Xiao Y, Ma WJ, Lu N, Wang Z, Wang N, Zhai WJ, Kong LS, Qu GZ, Wang QX, Wang JH (2019). Genetic variation of growth traits and genotype-by-environment interactions in clones of Catalpa bungei and Catalpa fargesii f. duclouxii. Forests, 10, 57. DOI: 10.3390/f10010057. |
[49] | Xiao Y, Wang JH, Yun HL, Yang GJ, Ma JW, Ma WJ, Qu GZ (2021). Genetic evaluation and combined selection for the simultaneous improvement of growth and wood properties in Catalpa bungei clones. Forests, 12, 868. DOI: 10.3390/f12070868. |
[50] | Xie L, Fu L, Widagdo FRA, Dong L, Li F (2022). Improving the accuracy of tree biomass estimations for three coniferous tree species in Northeast China. Trees, 36, 451-469. |
[51] | Zeng WS, Chen XY, Yang XY (2021). Developing national and regional individual tree biomass models and analyzing impact of climatic factors on biomass estimation for poplar plantations in China. Trees, 35, 93-102. |
[52] | Zhao HB, Zhou GY, Li ZJ, Qiu ZJ, Wu ZM, Wang X (2022). Biomass allocation and allometric growth models of four common tree species in southern subtropical evergreen broad-leaved forest. Scientia Silvae Sinicae, 58(2), 23-31. |
[赵厚本, 周光益, 李兆佳, 邱治军, 吴仲民, 王旭 (2022). 南亚热带常绿阔叶林4个常见树种的生物量分配特征与异速生长模型. 林业科学, 58(2), 23-31.] | |
[53] | Zhao JN (2020). Growth Regularity and Cultivation Technology of Catalpa bungei Plantation. Master degree dissertation, South China Agricultural University, Guangzhou. |
[赵江宁 (2020). 楸树人工林生长规律与关键培育技术研究. 硕士学位论文, 华南农业大学, 广州.] | |
[54] | Zheng CH, Mason EG, Jia LM, Wei SP, Sun CW, Duan J (2015). A single-tree additive biomass model of Quercus variabilis Blume forests in North China. Trees, 29, 705-716. |
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