林业科学 ›› 2026, Vol. 62 ›› Issue (2): 15-24.doi: 10.11707/j.1001-7488.LYKX20250256
• 前沿热点 • 上一篇
田惠玲1,朱建华2,何潇1,陈新云3,王冉4,肖文发2,雷相东1,*(
)
收稿日期:2025-04-27
修回日期:2025-06-16
出版日期:2026-02-25
发布日期:2026-03-04
通讯作者:
雷相东
E-mail:xdlei@ifrit.ac.cn
基金资助:
Huiling Tian1,Jianhua Zhu2,Xiao He1,Xinyun Chen3,Ran Wang4,Wenfa Xiao2,Xiangdong Lei1,*(
)
Received:2025-04-27
Revised:2025-06-16
Online:2026-02-25
Published:2026-03-04
Contact:
Xiangdong Lei
E-mail:xdlei@ifrit.ac.cn
摘要:
目的: 融合立地因子、林龄与林分密度效应,构建中亚热带典型森林类型林分乔木碳储量生长模型,精准分析林分碳储量生长变化,为森林生长量精准估测、森林经营方案优化以及森林碳汇潜力预估等提供指导。方法: 以我国中亚热带典型森林类型为研究对象,利用森林资源连续清查的3.07万个3期乔木林固定样地调查数据,采用基于林分平均高生长的分级算法划分立地等级,以平均林龄、立地等级、林分密度指数等因子为解释变量,按区域、优势树种(组)构建不同林分起源碳储量生长模型,分析林分碳储量生长变化规律。结果: 1) 中亚热带各林分平均高生长模型决定系数(R2)均达0.931及以上,树高总生长量随立地等级增加而增加,5个立地等级的高生长累积量水平接近等差数列,具有很好的分级结果。2) 基于平均林龄、立地等级、林分密度指数的林分碳储量生长模型决定系数(R2)均达0.633及以上。不同林分起源碳储量生长模型的建模精度存在差异:对于针叶纯林,该模型在人工林中的拟合效果优于天然林;对于混交林,该模型在天然林中的拟合效果优于人工林;针叶树种比阔叶树种具有更好的拟合效果。3) 各林分碳储量生长模型不同立地等级下林分碳储量的渐近值均呈a1 > a2 > a3 > a4 > a5的趋势,且5个立地等级的林分碳储量接近等差数列。天然林每公顷林分碳储量极限值整体高于人工林,阔叶混交林在不同林分起源下均具有较高的林分碳储量。4) 中立地等级条件下,人工林和天然林林分碳储量均随林龄增加而增大,并在近、成熟龄阶段开始趋于平稳。人工林林分碳储量的渐近值比天然林更早到达拐点林龄。结论: 本研究构建的各森林类型林分平均高生长模型和林分碳储量生长模型具有较好的拟合效果和较高的预估精度,含起源、林龄、立地等级、林分密度指数的林分碳储量生长模型可满足中亚热带区域主要树种(组)不同立地等级下林分碳储量随年龄动态变化预测的需要,还可用于编制该区域典型森林碳计量数表。
中图分类号:
田惠玲,朱建华,何潇,陈新云,王冉,肖文发,雷相东. 中亚热带典型森林类型林分乔木碳储量生长模型[J]. 林业科学, 2026, 62(2): 15-24.
Huiling Tian,Jianhua Zhu,Xiao He,Xinyun Chen,Ran Wang,Wenfa Xiao,Xiangdong Lei. Growth Model of Arbor Carbon Storage in Typical Forest Stands in the Mid-Subtropical Zone of China[J]. Scientia Silvae Sinicae, 2026, 62(2): 15-24.
表1
建模样本林分因子概况"
| 起源Origin | 变量Variables | 平均值Mean | 最小值Min. | 最大值Max. | 标准差SD |
| 人工林 Plantation | 林分平均年龄Stand mean age (A)/a | 19.4 | 5 | 68 | 9.6 |
| 林分平均高Stand mean height (H)/m | 9.2 | 1.3 | 26 | 3.3 | |
| 平均胸径Mean diameter (Dg)/cm | 11.0 | 7.4 | 26.1 | 2.7 | |
| 林分密度指数Stand density index (SDI)/(tree·hm?2) | 639.5 | 43.1 | 3 226.1 | 398.0 | |
| 林分公顷蓄积量Stand stock volume/(m3·hm?2) | 74.5 | 0.1 | 595.9 | 63.1 | |
| 林分碳储量Stand carbon storage/(t·hm?2) | 31.1 | 0.2 | 116.1 | 17. 6 | |
| 天然林 Natural forest | 林分平均年龄Stand mean age (A)/a | 26.3 | 5 | 120 | 13.7 |
| 林分平均高Stand mean height (H)/m | 9.3 | 1.3 | 28 | 3.1 | |
| 平均胸径Mean diameter (Dg)/cm | 11.1 | 7.6 | 38 | 3.0 | |
| 林分密度指数Stand density index (SDI)/(tree·hm?2) | 554. 5 | 45.1 | 2 410. 6 | 312.8 | |
| 林分公顷蓄积量Stand stock volume/(m3·hm?2) | 76.5 | 0.3 | 567.9 | 62.4 | |
| 林分碳储量Stand carbon storage/(t·hm?2) | 36.8 | 0.6 | 261.1 | 25.7 |
表2
立地因子等级划分标准"
| 因子Factor | 划分条件Classification criteria |
| 海拔Elevation | 200 m一个等级 A class per 200 m |
| 坡度Slope | 10°一个等级 A class per 10° |
| 坡向Aspect | 北坡 North;东北坡 Northeast;东坡 East;东南坡Southeast;南坡 South; 西南坡 Southwest;西坡 West;西北坡 Northwest;无坡向 No aspect |
| 坡位Slope position | 脊部 Ridge;上坡 Upper;中坡 Middle;下坡 Lower;山谷(或山洼) Valley;平地 Flat |
| 土层厚度Soil depth | 20 cm一个等级 A class per 20 cm |
| 腐殖层厚度Humus depth | 薄Thin:<2 cm;中Moderate:2~5 cm;厚Thick:>5 cm |
表3
典型森林类型不同立地等级林分平均高生长模型的参数估计值及拟合优度"
| 起源 Origin | 森林类型 Forest type | 参数估计值 Parameter estimates | 评价指标 Evaluation indices | |||||||||
| a1 | a2 | a3 | a4 | a5 | b | c | R2 | RMSE | rRMSE(%) | |||
| 人工林 Plantation | 华山松 Pinus armandii | 16.5 | 13.0 | 10.5 | 7.70 | 5.01 | 0.050 00 | 0.762 | 0.955 | 0.691 | 8.46 | |
| 马尾松 Pinus massoniana | 44.6 | 34.7 | 27.6 | 21.30 | 14.50 | 0.007 00 | 0.589 | 0.958 | 0.760 | 7.84 | ||
| 湿地松 Pinus elliottii | 20.9 | 16.4 | 13.6 | 11.30 | 8.04 | 0.057 70 | 1.160 | 0.967 | 0.584 | 7.07 | ||
| 杉木Cunninghamia lanceolata | 22.4 | 17.5 | 13.8 | 10.70 | 7.42 | 0.043 40 | 0.790 | 0.953 | 0.707 | 7.93 | ||
| 柏木Cupressus funebris | 17.0 | 13.5 | 10.9 | 8.70 | 6.42 | 0.097 50 | 1.370 | 0.932 | 0.704 | 7.38 | ||
| 桉树 Eucalyptus spp. | 18.8 | 15.0 | 11.6 | 8.72 | 5.72 | 0.467 00 | 1.300 | 0.950 | 0.863 | 7.99 | ||
| 其他软阔类 Other soft broadleaf | 22.6 | 17.0 | 13.1 | 10.20 | 6.74 | 0.160 00 | 1.380 | 0.952 | 0.911 | 8.87 | ||
| 针叶混交林 Mixed coniferous | 18.7 | 14.9 | 12.2 | 9.75 | 7.19 | 0.052 30 | 0.757 | 0.950 | 0.663 | 7.00 | ||
| 阔叶混交林 Mixed broadleaf | 17.7 | 13.5 | 10.9 | 8.22 | 5.69 | 0.175 00 | 1.570 | 0.949 | 0.801 | 8.62 | ||
| 针阔混交林 Mixed coniferous and broadleaf | 23.3 | 18.1 | 14.6 | 11.50 | 7.86 | 0.014 00 | 0.365 | 0.931 | 0.736 | 8.29 | ||
| 天然林 Natural forest | 马尾松 Pinus massoniana | 44.3 | 34.6 | 27.6 | 21.20 | 14.70 | 0.007 79 | 0.592 | 0.944 | 0.884 | 8.61 | |
| 高山松 Pinus densata | 23.0 | 17.5 | 12.4 | 8.93 | 4.70 | 0.044 10 | 1.220 | 0.979 | 0.837 | 6.92 | ||
| 杉木 Cunninghamia lanceolata | 17.8 | 14.1 | 11.3 | 8.90 | 6.31 | 0.046 00 | 0.659 | 0.946 | 0.629 | 7.47 | ||
| 柏木 Cupressus funebris | 15.0 | 12.5 | 10.4 | 8.49 | 6.06 | 0.091 30 | 1.720 | 0.942 | 0.672 | 6.64 | ||
| 栎类 Quercus spp. | 23.4 | 17.3 | 13.7 | 10.80 | 7.56 | 0.013 80 | 0.448 | 0.952 | 0.800 | 8.85 | ||
| 其他硬阔类 Other hard broadleaf | 24.4 | 18.2 | 14.5 | 11.30 | 8.17 | 0.005 85 | 0.277 | 0.940 | 0.806 | 8.68 | ||
| 针叶混交林 Mixed coniferous | 31.6 | 24.2 | 19.4 | 15.30 | 10.90 | 0.010 90 | 0.529 | 0.943 | 0.717 | 7.51 | ||
| 阔叶混交林 Mixed broadleaf | 27.4 | 20.9 | 16.8 | 13.40 | 9.89 | 0.011 90 | 0.485 | 0.945 | 0.688 | 7.59 | ||
| 针阔混交林 Mixed coniferous and broadleaf | 35.4 | 27.0 | 21.1 | 16.50 | 12.00 | 0.008 31 | 0.521 | 0.943 | 0.687 | 7.63 | ||
表4
典型森林类型不同立地等级林分乔木碳储量生长模型的参数估计值及拟合优度"
| 起源 Origin | 森林类型 Forest type | 样本数 Sample size | 参数估计值 Parameter estimates | 评价指标 Evaluation indices | ||||||||||
| a1 | a2 | a3 | a4 | a5 | b1 | b2 | c | R2 | RMSE | rRMSE(%) | ||||
| 人工林 Plantation | 华山松 Pinus armandii | 230 | 102.10 | 92.34 | 87.18 | 78.77 | 63.50 | 0.525 50 | 1.834 0 | 0.349 2 | 0.811 9 | 7.758 | 24.02 | |
| 马尾松 Pinus massoniana | 1 622 | 119.40 | 107.80 | 89.28 | 77.61 | 61.68 | 0.202 10 | 1.187 0 | 0.528 0 | 0.768 9 | 9.751 | 30.86 | ||
| 湿地松 Pinus elliottii | 374 | 70.84 | 65.58 | 61.12 | 57.57 | 42.79 | 1.754 00 | 1.762 0 | 0.408 2 | 0.777 1 | 5.588 | 25.95 | ||
| 杉木Cunninghamia lanceolata | 5 833 | 104.80 | 89.91 | 79.95 | 70.15 | 55.32 | 0.264 50 | 1.258 0 | 0.455 6 | 0.816 2 | 7.463 | 23.74 | ||
| 柏木Cupressus funebris | 631 | 52.09 | 54.93 | 50.29 | 47.63 | 44.87 | 0.938 70 | 1.359 0 | 0.366 9 | 0.695 6 | 6.274 | 19.55 | ||
| 桉树 Eucalyptus spp. | 302 | 51.53 | 47.39 | 38.04 | 28.04 | 26.26 | 2.538 00 | 1.130 0 | 0.531 7 | 0.758 4 | 5.659 | 28.48 | ||
| 其他软阔类 Other soft broadleaf | 269 | 64.81 | 59.33 | 49.34 | 45.39 | 37.53 | 1.764 00 | 1.002 0 | 0.701 9 | 0.656 2 | 10.02 | 34.00 | ||
| 针叶混交林 Mixed coniferous | 1 127 | 79.44 | 74.11 | 70.02 | 62.21 | 54.20 | 0.430 20 | 1.510 0 | 0.313 8 | 0.784 2 | 6.659 | 19.50 | ||
| 阔叶混交林 Mixed broadleaf | 355 | 110.10 | 96.48 | 85.34 | 76.64 | 56.96 | 0.432 20 | 1.218 0 | 0.552 4 | 0.670 9 | 11.270 | 42.79 | ||
| 针阔混交林 Mixed coniferous and broadleaf | 1 141 | 129.10 | 115.50 | 99.41 | 91.16 | 70.14 | 0.177 60 | 1.154 0 | 0.482 3 | 0.712 5 | 10.510 | 32.47 | ||
| 天然林 Natural forest | 马尾松 Pinus massoniana | 4 877 | 128.10 | 116.70 | 100.9 | 85.98 | 70.71 | 0.154 30 | 1.111 0 | 0.562 0 | 0.748 9 | 9.352 | 30.03 | |
| 高山松 Pinus densata | 112 | 123.80 | 103.40 | 79.90 | 72.34 | 53.46 | 0.277 40 | 1.214 0 | 0.449 6 | 0.906 1 | 7.423 | 14.06 | ||
| 杉木 Cunninghamia lanceolata | 1 508 | 76.05 | 71.85 | 64.18 | 56.45 | 48.54 | 0.268 30 | 1.070 0 | 0.529 6 | 0.795 2 | 6.021 | 24.71 | ||
| 柏木 Cupressus funebris | 554 | 47.80 | 46.77 | 43.61 | 39.75 | 33.74 | 0.584 40 | 0.931 9 | 0.534 6 | 0.633 0 | 7.196 | 22.26 | ||
| 栎类 Quercus spp. | 1 773 | 249.60 | 223.50 | 205.70 | 195.10 | 169.8 | 0.144 60 | 1.336 0 | 0.633 9 | 0.762 4 | 18.890 | 41.15 | ||
| 其他硬阔类 Other hard broadleaf | 847 | 262.60 | 230.10 | 219.50 | 187.90 | 174.30 | 0.060 45 | 1.407 0 | 0.442 4 | 0.768 0 | 14.170 | 31.52 | ||
| 针叶混交林 Mixed coniferous | 1 704 | 83.02 | 79.02 | 73.59 | 67.07 | 60.68 | 0.248 00 | 1.284 0 | 0.377 3 | 0.792 6 | 5.898 | 18.21 | ||
| 阔叶混交林 Mixed broadleaf | 8 290 | 233.50 | 207.00 | 181.70 | 162.90 | 139.40 | 0.096 58 | 0.992 7 | 0.707 6 | 0.729 5 | 15.560 | 37.21 | ||
| 针阔混交林 Mixed coniferous and broadleaf | 3 385 | 130.90 | 119.00 | 108.70 | 95.32 | 83.49 | 0.166 60 | 1.075 0 | 0.558 8 | 0.733 8 | 9.290 | 27.39 | ||
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