林业科学 ›› 2026, Vol. 62 ›› Issue (5): 69-79.doi: 10.11707/j.1001-7488.LYKX20250344
收稿日期:2025-05-29
修回日期:2026-03-10
出版日期:2026-05-10
发布日期:2026-05-12
通讯作者:
董灵波
E-mail:farrell0503@126.com
基金资助:
Dongyuan Tian,Zhaogang Liu,Lichun Jiang,Lingbo Dong*(
)
Received:2025-05-29
Revised:2026-03-10
Online:2026-05-10
Published:2026-05-12
Contact:
Lingbo Dong
E-mail:farrell0503@126.com
摘要:
目的: 构建随机森林模型,识别大兴安岭中部地区天然林更新数量的关键影响因素,为该地区森林的可持续经营提供理论依据。方法: 基于新林林业局翠岗林场、新林林场和壮志林场共96块标准样地调查数据,从林分特征、立地条件、土壤条件、林木大小多样性、物种多样性和林分空间结构6方面选取29个基础指标,采用Poisson模型、负二项模型和随机森林算法分别构建兴安落叶松和白桦更新数量模型;经模型选优后,应用OOB置换法确定候选变量对兴安落叶松和白桦更新数量的贡献。结果: 十折交叉检验表明,随机森林更新数量预测模型精度显著高于Poisson模型和负二项模型,其中兴安落叶松和白桦随机森林更新数量模型的均方根误差(RMSE)分别为482和682 tree·hm?2,平均绝对误差(MAE)分别为377和460 tree·hm?2。经OOB置换法得出各变量的相对重要性,其中对兴安落叶松更新数量重要的变量依次为胸径Shannon指数(17.57%)、胸径Pielou均匀度指数(16.88%)、单位蓄积量(13.29%)、胸径Simpson指数(12.92%)和林分平均胸径(12.91%);对白桦更新数量重要的变量依次为胸径Shannon指数(18.53%)、胸径Pielou均匀度指数(16.13%)、草本盖度(12.62%)、林分平均胸径(12.34%)和灌木盖度(11.31%)。结论: 林木大小多样性和林分密度是大兴安岭中部地区天然林更新数量的重要影响因子,可通过抚育间伐或补植方式确保科学合理的林分密度,进而促进天然更新和森林生态系统的自然演替。
中图分类号:
田栋元,刘兆刚,姜立春,董灵波. 基于随机森林的大兴安岭中部天然林更新数量影响因素识别[J]. 林业科学, 2026, 62(5): 69-79.
Dongyuan Tian,Zhaogang Liu,Lichun Jiang,Lingbo Dong. Identification of the Influencing Factors on the Regeneration Quantity of Natural Forests in the Central Part of Daxing’anling Mountains Based on Random Forest[J]. Scientia Silvae Sinicae, 2026, 62(5): 69-79.
表1
各样地基本特征"
| 项 Item | 变量 Variables | 最小值 Min. | 平均值 Mean | 最大值 Max. | 标准差 SD | 变异系数 CV (%) |
| 林分特征 Stand characteristics | 平均胸径Mean DBH/cm | 9.50 | 13.37 | 21.10 | 2.63 | 19.67 |
| 平均树高Mean height/m | 8.80 | 11.75 | 18.20 | 2.13 | 18.13 | |
| 林木密度Tree density/( tree·hm?2) | 567.00 | 1 466.00 | 2 680.00 | 543.33 | 37.06 | |
| 单位蓄积量Volume/(m3·hm?2) | 53.47 | 127.58 | 223.11 | 39.40 | 30.88 | |
| 郁闭度Canopy density | 0.25 | 0.63 | 0.90 | 0.12 | 19.05 | |
| 灌木盖度Shrub coverage (%) | 0.00 | 15.48 | 84.00 | 20.07 | 129.65 | |
| 草本盖度Herb coverage (%) | 0.03 | 19.99 | 84.25 | 25.82 | 129.16 | |
| 立地条件 Site conditions | 海拔Elevation/m | 404.00 | 514.45 | 676.30 | 67.66 | 13.15 |
| 坡度Slope | 0.00 | 7.00 | 25.00 | 6.41 | 0.92 | |
| 坡向Aspect | 1.00 | 4.96 | 8.00 | 2.52 | 50.75 | |
| 坡位Site | 1.00 | 2.03 | 3.00 | 0.62 | 30.52 | |
| 土壤条件 Soil conditions | 酸碱度pH | 4.03 | 5.28 | 6.41 | 0.40 | 7.63 |
| OM/(g·kg?1) | 1.01 | 4.50 | 6.81 | 18.10 | 30.06 | |
| TN/(g·kg?1) | 0.67 | 3.21 | 9.11 | 1.68 | 52.36 | |
| TP/(g·kg?1) | 1.21 | 1.53 | 2.46 | 0.24 | 15.46 | |
| TK/(g·kg?1) | 6.14 | 8.28 | 10.85 | 1.28 | 15.41 | |
| 林木大小多样性 Tree size diversity | DSW | 1.54 | 2.11 | 2.89 | 0.27 | 13.03 |
| DS | 0.76 | 0.86 | 0.96 | 0.04 | 4.66 | |
| DP | 0.72 | 0.88 | 1.00 | 0.07 | 7.45 | |
| HSW | 1.23 | 1.76 | 2.12 | 0.18 | 10.52 | |
| HS | 0.67 | 0.80 | 0.87 | 0.04 | 5.07 | |
| HP | 0.72 | 0.87 | 0.99 | 0.06 | 6.45 | |
| 物种多样性 Species diversity | TSSW | 0.05 | 0.66 | 1.19 | 0.25 | 37.96 |
| TSS | 0.02 | 0.39 | 0.64 | 0.14 | 37.19 | |
| TSP | 0.07 | 0.63 | 1.00 | 0.20 | 32.18 | |
| 林分空间结构 Stand spatial structure | W | 0.41 | 0.50 | 0.75 | 0.05 | 9.12 |
| U | 0.39 | 0.50 | 0.70 | 0.04 | 8.21 | |
| M | 0.03 | 0.34 | 0.61 | 0.14 | 40.45 | |
| SDP | 0.00 | 0.63 | 1.00 | 0.39 | 61.93 | |
| 更新数量 Regeneration number | 兴安落叶松 Larix gmelinii /( tree·hm?2) | 90.00 | 899.00 | 4 550.00 | 999.39 | 111.17 |
| 白桦Betula platyphylla /( tree·hm?2) | 40.00 | 1 035.00 | 7 800.00 | 1 406.53 | 135.90 |
图1
更新数量特征变量选取 MDBH: 林分平均胸径Mean stand DBH; MH: 林分平均树高Mean stand tree height; V: 单位蓄积量Stand volume; TD: 林分密度Stand density; CD: 郁闭度Canopy density; SL: 坡度Slope; AS: 坡向Aspect; SI: 坡位Site; ELE: 海拔Elevation; SC: 灌木盖度Shrub coverage; HC: 草本盖度Herb coverage; OM: 有机质Organic matter; TN: 全氮Total N; TP: 全磷Total P; TK: 全钾Total K; DSW: 胸径Shannon指数Shannon index of DBH; DS: 胸径Simpson指数Simpson index of DBH; DP: 胸径Pielou均匀度指数Pielou evenness index of DBH; HSW: 树高Shannon指数Shannon index of height; HS: 树高Simpson指数Simpson index of height; HP: 树高Pielou均匀度指数Pielou evenness index of height; TSSW: 树种Shannon指数Shannon index of tree species; TSS: 树种Simpson指数Simpson index of tree species; TSP: 树种Pielou均匀度指数Pielou evenness index of tree species; W: 角尺度Uniform angle index; U: 大小比数Neighborhood comparison; M: 混交度Mingling degree; SDP: 空间分布方式Spatial distribution pattern."
表2
Poisson模型和负二项模型参数估计及显著性"
| 参数Parameter | 兴安落叶松Larix gmelinii | 白桦Betula platyphylla | |||||||||||
| Poisson | P | VIF | NB | P | VIF | Poisson | P | VIF | NB | P | VIF | ||
| 截距Intercept | 4.228 0 | *** | 7.114 1 | *** | 2.034 0 | *** | 2.534 4 | *** | |||||
| ELE | ?0.003 1 | *** | 2.082 2 | ?0.004 7 | *** | 1.499 2 | |||||||
| OM | 0.048 1 | *** | 1.548 0 | ||||||||||
| TP | ?1.755 0 | *** | 4.955 3 | ?0.887 5 | * | 1.532 0 | |||||||
| TK | 0.043 8 | *** | 4.108 5 | ||||||||||
| DSW | 1.567 5 | *** | 1.045 8 | 0.826 0 | *** | 8.115 0 | |||||||
| DS | 4.685 0 | *** | 3.719 1 | ||||||||||
| DP | 2.855 0 | *** | 4.215 4 | ||||||||||
| HSW | 0.169 8 | *** | 1.619 5 | 0.947 4 | * | 1.449 0 | |||||||
| MDBH | 0.230 6 | *** | 2.112 5 | ||||||||||
| MH | 0.132 1 | *** | 5.671 0 | 0.028 7 | *** | 5.523 9 | |||||||
| TD | ?0.000 1 | *** | 3.191 4 | ?0.000 5 | *** | 3.210 8 | |||||||
| V | 0.001 1 | *** | 3.570 9 | 0.001 3 | *** | 3.851 6 | ?0.006 0 | * | 1.657 2 | ||||
| M | 1.270 0 | *** | 1.054 7 | ||||||||||
| SC | 0.002 9 | *** | 1.822 5 | ||||||||||
| HC | 0.007 4 | *** | 2.486 3 | 0.006 4 | * | 1.368 8 | |||||||
图4
基于OOB置换法的相对重要性 DSW: 胸径Shannon指数Shannon index of DBH; DP: 胸径Pielou均匀度指数Pielou evenness index of DBH; V: 单位蓄积量Stand volume; DS: 胸径Simpson指数Simpson index of DBH; HSW: 树高Shannon指数Shannon index of height; MDBH: 林分平均胸径Mean stand DBH; M: 混交度Mingling degree; MH: 林分平均树高Mean stand tree height; OM: 有机质Organic matter; ELE: 海拔Elevation; TD: 林分密度Stand density; TP: 全磷Total P; TK: 全钾Total K; HC: 草本盖度Herb coverage; SC: 灌木盖度Shrub coverage."
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