林业科学 ›› 2026, Vol. 62 ›› Issue (9): 82-95.doi: 10.11707/j.1001-7488.LYKX20250741
收稿日期:2025-12-11
出版日期:2026-09-10
发布日期:2026-09-23
通讯作者:
景维鹏
E-mail:jwp@nefu.edu.cn
基金资助:
Hailiang Lu,Weitao Zou,Chao Li,Guangsheng Chen,Weipeng Jing*(
)
Received:2025-12-11
Online:2026-09-10
Published:2026-09-23
Contact:
Weipeng Jing
E-mail:jwp@nefu.edu.cn
摘要:
目的: 为提升森林扰动检测精度,采用多源遥感数据融合获取时空连续的Landsat影像数据,提出基于Landsat影像与深度时序建模的森林扰动检测方法(LTFD)。以大兴安岭呼中区火灾与采伐扰动为例,分析多源融合影像的应用潜力,探究深度学习模型在长时序扰动检测中的优势,为区域森林扰动检测和森林可持续经营提供技术参考。方法: 首先,构建2000—2022年呼中区时空连续的Landsat月合成数据集,通过MODIS 500 m和250 m波段影像开展空谱融合,生成MODIS 250 m多光谱影像,将其与Landsat影像进行时空融合,实现对Landsat云遮挡缺失区域的时空重建,该数据集共包含92幅影像,为后续森林扰动检测提供高时间分辨率数据支撑。其次,引入适用于深度时序建模的Transformer模型进行扰动检测,以全球森林扰动产品为核心,构建大规模训练样本作为模型监督信息,为准确获取扰动开始时间,采用归一化燃烧指数(NBR)阈值法逐像元进行提取。最后,基于呼中地区目视解译的火灾与采伐样本对LTFD方法开展精度验证,并以LandTrendr和随机森林(RF)作为对比算法进行性能评估。结果: 从定量评估和可视化分析2方面对比LTFD方法与LandTrendr和RF方法的检测性能。LTFD 方法基于深度时序建模策略,在构建的月合成数据集上可显著提升森林扰动检测精度,同时在空间可视化结果中对扰动范围和形态的刻画更为准确和细致。定量评估结果表明,构建的月合成数据集对不同扰动检测方法的精度影响存在显著差异,对LandTrendr算法产生负面影响,总体精度(OA)为0.852,Kappa系数为0.498,总体时间精度(TOA)仅为0.088,表现最差,表明该方法分段线性拟合方式难以有效检测扰动发生时间;对RF和LTFD方法具有积极作用,其中基于LTFD方法表现最优,OA达0.895,Kappa系数为0.701,TOA为0.767,表明Transformer模型凭借自注意力机制在时序依赖和非线性建模方面具有优势。结论: 本研究验证多源遥感数据融合技术与深度学习模型相结合在提升森林扰动检测精度方面的可行性和有效性,为构建高精度、智能化的森林扰动检测体系提供了新的技术路径和方法参考,有助于推动区域尺度森林扰动检测向精细化和智能化方向发展。
中图分类号:
路海亮,邹为涛,李超,陈广胜,景维鹏. 基于多源数据融合与深度时序建模的森林扰动检测方法[J]. 林业科学, 2026, 62(9): 82-95.
Hailiang Lu,Weitao Zou,Chao Li,Guangsheng Chen,Weipeng Jing. Forest Disturbance Detection Method Based on Multi-source Data Fusion and Deep Temporal Modeling[J]. Scientia Silvae Sinicae, 2026, 62(9): 82-95.
表4
不同光谱指数组合输入的LTFD扰动检测结果①"
| 光谱指数组合 Spectral index combination | 扰动分类 Disturbance classification | 参考数据Reference | UA | PA | OA | Kappa | |
| 非扰动Undisturbed | 扰动Disturbed | ||||||
| NBR | 非扰动Undisturbed | 726 | 53 | 0.931 | 0.932 | 0.890 | 0.656 |
| 扰动Disturbed | 54 | 141 | 0.727 | 0.723 | |||
| NBR+EVI | 非扰动Undisturbed | 704 | 26 | 0.903 | 0.964 | 0.895 | 0.701 |
| 扰动Disturbed | 76 | 168 | 0.866 | 0.689 | |||
| NBR+NDMI | 非扰动Undisturbed | 704 | 37 | 0.903 | 0.950 | 0.884 | 0.662 |
| 扰动Disturbed | 76 | 157 | 0.809 | 0.674 | |||
| NBR+NDMI+EVI | 非扰动Undisturbed | 693 | 22 | 0.888 | 0.969 | 0.888 | 0.688 |
| 扰动Disturbed | 87 | 172 | 0.887 | 0.664 | |||
表5
不同扰动检测方法验证结果①"
| 方法 Methods | 扰动分类 Disturbance classification | 参考数据Reference | UA | PA | OA | Kappa | TOA | |
| 非扰动Undisturbed | 扰动Disturbed | |||||||
| LandTrendr-Y | 非扰动Undisturbed | 763 | 89 | 0.978 | 0.896 | 0.891 | 0.604 | 0.686 |
| 扰动Disturbed | 17 | 105 | 0.541 | 0.861 | ||||
| LandTrendr-M | 非扰动Undisturbed | 728 | 92 | 0.933 | 0.888 | 0.852 | 0.498 | 0.088 |
| 扰动Disturbed | 52 | 102 | 0.526 | 0.662 | ||||
| RF | 非扰动Undisturbed | 665 | 24 | 0.853 | 0.965 | 0.857 | 0.620 | 0.742 |
| 扰动Disturbed | 115 | 170 | 0.876 | 0.596 | ||||
| LTFD | 非扰动Undisturbed | 704 | 26 | 0.903 | 0.964 | 0.895 | 0.701 | 0.767 |
| 扰动Disturbed | 76 | 168 | 0.866 | 0.689 | ||||
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