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利用无人机RGB影像在物种水平上估算湿地植被地上生物量。

Aboveground biomass estimation of wetland vegetation at the species level using unoccupied aerial vehicle RGB imagery.

作者信息

Zhou Rui, Yang Chao, Li Enhua, Cai Xiaobin, Wang Xuelei

机构信息

Key Laboratory for Environment and Disaster Monitoring and Evaluation of Hubei, Innovation Academy for Precision Measurement Science and Technology, Chinese Academy of Sciences, Wuhan, China.

University of Chinese Academy of Sciences, Beijing, China.

出版信息

Front Plant Sci. 2023 Jul 17;14:1181887. doi: 10.3389/fpls.2023.1181887. eCollection 2023.

DOI:10.3389/fpls.2023.1181887
PMID:37528979
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC10388590/
Abstract

Wetland vegetation biomass is an essential indicator of wetland health, and its estimation has become an active area of research. () is the dominant species of emergent vegetation in Honghu Wetland, and monitoring its aboveground biomass (AGB) can provide a scientific basis for the protection and restoration of this and other wetlands along the Yangtze River. This study aimed to develop a method for the AGB estimation of in Honghu Wetland using high-resolution RGB imagery acquired from an unoccupied aerial vehicle (UAV). The spatial distribution of was first extracted through an object-based classification method using the field survey data and UAV RGB imagery. Linear, quadratic, exponential and back propagation neural network (BPNN) models were constructed based on 17 vegetation indices calculated from RGB images to invert the AGB. The results showed that: (1) The visible vegetation indices were significantly correlated with the AGB of . The absolute value of the correlation coefficient between the AGB and CIVE was 0.87, followed by ExG (0.866) and COM2 (0.837). (2) Among the linear, quadratic, and exponential models, the quadric model based on CIVE had the highest inversion accuracy, with a validation R of 0.37, RMSE and MAE of 853.76 g/m and 671.28 g/m, respectively. (3) The BPNN model constructed with eight factors correlated with the AGB had the best inversion effect, with a validation R of 0.68, RMSE and MAE of 732.88 g/m and 583.18 g/m, respectively. ​Compared to the quadratic model constructed by CIVE, the BPNN model achieved better results, with a reduction of 120.88 g/m in RMSE and 88.10 g/m in MAE. This study indicates that using UAV-based RGB images and the BPNN model provides an effective and accurate technique for the AGB estimation of dominant wetland species, making it possible to efficiently and dynamically monitor wetland vegetation cost-effectively.

摘要

湿地植被生物量是湿地健康状况的重要指标,其估算已成为一个活跃的研究领域。()是洪湖湿地挺水植被的优势物种,监测其地上生物量(AGB)可为该湿地及长江沿线其他湿地的保护与恢复提供科学依据。本研究旨在利用从无人机(UAV)获取的高分辨率RGB影像,开发一种估算洪湖湿地()地上生物量的方法。首先通过基于对象的分类方法,利用实地调查数据和无人机RGB影像提取()的空间分布。基于从RGB图像计算得到的17种植被指数构建线性、二次、指数和反向传播神经网络(BPNN)模型,以反演地上生物量。结果表明:(1)可见光植被指数与()的地上生物量显著相关。地上生物量与CIVE之间的相关系数绝对值为0.87,其次是ExG(0.866)和COM2(0.837)。(2)在线性、二次和指数模型中,基于CIVE的二次模型反演精度最高,验证R为0.37,RMSE和MAE分别为853.76 g/m和671.28 g/m。(3)由与地上生物量相关的8个因子构建的BPNN模型反演效果最佳,验证R为0.68,RMSE和MAE分别为732.88 g/m和583.18 g/m。与由CIVE构建的二次模型相比,BPNN模型效果更好,RMSE降低了120.88 g/m,MAE降低了88.10 g/m。本研究表明,利用基于无人机的RGB图像和BPNN模型为湿地优势物种地上生物量的估算提供了一种有效且准确的技术,使得以具有成本效益的方式高效、动态地监测湿地植被成为可能。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/1ae2225ab079/fpls-14-1181887-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/04c3c628ec30/fpls-14-1181887-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/b55ec5082aac/fpls-14-1181887-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/efafeb2e4f90/fpls-14-1181887-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/83034be572f7/fpls-14-1181887-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/da7122af8399/fpls-14-1181887-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/7022c4fe2a44/fpls-14-1181887-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/2d2bbe998f6d/fpls-14-1181887-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/1ae2225ab079/fpls-14-1181887-g008.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/04c3c628ec30/fpls-14-1181887-g001.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/b55ec5082aac/fpls-14-1181887-g002.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/efafeb2e4f90/fpls-14-1181887-g003.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/83034be572f7/fpls-14-1181887-g004.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/da7122af8399/fpls-14-1181887-g005.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/7022c4fe2a44/fpls-14-1181887-g006.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/2d2bbe998f6d/fpls-14-1181887-g007.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/2f77/10388590/1ae2225ab079/fpls-14-1181887-g008.jpg

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