1. Development and Research Center, China Geological Survey, Beijing 100037, China
2. School of Earth Science and Resources, China University of Geosciences (Beijing), Beijing 100083, China
3. National Geological Archives of China,Beijing 100037,China
4. College of Geoscience and Surveying Engineering, China University of Mining and Technology (Beijing), Beijing 100083, China
5. China Centre for Resources Satellite Data and Application, Beijing 100094, China
Abstract:To effectively obtain effective spectral response sub intervals of maize leaves under heavy metal lead pollution, and support heavy metal monitoring of crops. This article used hyperspectral remote sensing as the core technology and set up a maize pot experiment to collect a complete set of hyperspectral remote sensing data for maize leaves under heavy metal lead pollution using the SVC land cover spectrometer. A Lead Detection Index (LDI) was designed based on an improved Red Edge Normalization Index to obtain effective spectral response sub intervals of maize leaves under heavy metal lead pollution. Firstly, the original reflectance spectral data of maize in the training set was denoised by using the Db5 wavelet in the Daubechies wavelet series, resulting in the d5 component of the high-frequency component in the 5th layer of the wavelet decomposition. Then, we divided the entire spectral range of mazie leaves from 350 to 2 500 nm into 11 subband intervals and established LDI using the d5 wavelet coefficient values corresponding to the middle wavelength of each subband interval. Using the Pearson correlation coefficient r, LDI was compared with three conventional spectral indices (Photochemical Reflection Index, PRI; Meris Territorial Chlorophyll Index, MTCI; Modified Red Edge Simple Ratio Index, mSR). The effective spectral response sub-intervals of maize leaves under heavy metal lead pollution obtained from the training set data are purple valley, green peak, near-infrared platform, and near edge. The absolute values of Pearson correlation coefficients are all greater than 0.9, which are 0.911 0, 0.915 5, 0.905 1, and 0.907 6, respectively. In contrast, the absolute values of Pearson correlation coefficients between the three conventional spectral indices and the heavy metal lead content in the leaves are all less than 0.9, indicating high LDI effectiveness. Finally, we used the validation set data to obtain the effective spectral response subintervals of maize leaves under heavy metal lead pollution: purple valley, green peak, near-infrared platform, and near edge. The absolute Pearson correlation coefficients were all greater than 0.9. The Pearson correlation coefficients r for validation set one and validation set two were -0.999 9, -0.973 0, 0.914 2, 0.905 7, and -0.999 9, 0.911 7, -0.914 6, and 0.910 3, respectively. However, the absolute Pearson correlation coefficients between the three conventional spectral indices and the heavy metal lead content in the leaves were all less than 0.9. The results showed that under heavy metal lead pollution, the effective spectral response subbands of maize leaves were purple valley, green peak, near-infrared platform, and near-edge four subbands. The research results can provide technical support for monitoring heavy metal pollution in other crops.
张 超,杨可明,商云涛,牛颖超,夏 天. 矿区地质资料模拟铅污染环境下LDI诊断玉米敏感光谱区间[J]. 光谱学与光谱分析, 2025, 45(06): 1752-1758.
ZHANG Chao, YANG Ke-ming, SHANG Yun-tao, NIU Ying-chao, XIA Tian. Simulating Lead Pollution Environment Based on Geological Data of
Mining Areas LDI Diagnosis of Sensitive Spectral Range in Maize. SPECTROSCOPY AND SPECTRAL ANALYSIS, 2025, 45(06): 1752-1758.
[1] TIAN Wen, ZONG Da-peng, FANG Cheng-gang, et al(田 稳, 宗大鹏, 方成刚, 等). China Environmental Science(中国环境科学), 2022, 42(10): 4901.
[2] Su H F, Zhang Y Z, Lu Z C, et al. Journal of Cleaner Production, 2022, 373: 133825.
[3] Kendler R S, Mano Z, Aharoni R, et al. Scientific Reports, 2022, 12(1): 17580.
[4] SONG Hong-mei, LI Ting-liang, LIU Yang, et al (宋红梅, 李廷亮, 刘 洋, 等). Journal of Soil and Water Conservation(水土保持学报), 2023, 37(1): 332.
[5] HAN Tian-fu, LI Ya-zhen, QU Xiao-lin, et al(韩天富, 李亚贞, 曲潇林, 等). Transactions of the Chinese Society of Agricultural Engineering(农业工程学报), 2022, 38(1): 100.
[6] Blumberg A, Schodlok M C. International Journal of Applied Earth Observation and Geoinformation, 2022, 114: 103034.
[7] WU Qi, SUN Yang-ming, SANG Jun-wei, et al(邬 奇, 孙扬名, 桑俊伟, 等). Jiangsu Agricultural Sciences(江苏农业科学), 2024, 52(3): 47.
[8] Li Y R, Yang K M, Wu B, et al. Spectrochimica Acta Part A: Molecular and Biomolecular Spectroscopy, 2022, 278: 121318.
[9] GAO Wei, YANG Ke-ming, CHEN Gai-ying, et al(高 伟, 杨可明, 陈改英, 等). Transactions of the Chinese Society of Agricultural Engineering(农业工程学报), 2021, 37(3): 173.
[10] Zhang C Y, Ren H Z, Qin Q M, et al. Remote Sensing Letters, 2017, 8(6): 576.
[11] YANG Ke-ming, WANG Guo-ping, YOU Di, et al(杨可明, 汪国平, 尤 笛, 等). Spectroscopy and Spectral Analysis(光谱学与光谱分析), 2016, 36(8): 2568.
[12] Guo Z H, Zhang Y X, Xu R, et al. The Science of the Total Environment, 2023, 856(P2): 159264.
[13] Liu F, Wang F, Wang X Q, et al. Agronomy, 2022, 12(10): 2350.
[14] GUO Xiao-yan, YU Shuai-qing, SHEN Hang-chi, et al(郭小燕, 于帅卿, 沈航驰, 等). Transactions of the Chinese Society of Agricultural Machinery(农业机械学报), 2022, 53(12): 301.
[15] YU Hai-yang, XIE Sai-fei, GUO Ling-hui, et al(于海洋, 谢赛飞, 郭灵辉, 等). Transactions of the Chinese Society of Agricultural Machinery(农业机械学报), 2022, 53(8): 231.
[16] GUO Wen-juan, FENG Quan, LI Xiang-zhou, et al(郭文娟, 冯 全, 李相周, 等). Journal of Chinese Agricultural Mechanization(中国农机化学报), 2022, 43(10): 157.
[17] Wang Y Y, Xiong F, Zhang Y, et al. Food Chemistry, 2023, 404(Part A): 134503.
[18] LI Guo-xu, GENG Jing, XU Xuan-hong, et al(李国旭, 耿 静, 许选虹, 等). Transactions of the Chinese Society of Agricultural Engineering(农业工程学报), 2022, 38(12): 224.
[19] Newete S W, Erasmus B F N, Weiersbye I M, et al. International Journal of Remote Sensing, 2014, 35(3): 799.