欢迎访问《应用生态学报》官方网站,今天是 分享到:

应用生态学报 ›› 2016, Vol. 27 ›› Issue (6): 1775-1784.doi: 10.13287/j.1001-9332.201606.030

• 目次 • 上一篇    下一篇

基于Hyperion影像植被光谱的土壤重金属含量空间分布反演——以青海省玉树县为例

杨灵玉1, 高小红1*, 张 威1,2, 史飞飞1, 何林华1, 贾 伟1   

  1. 1青海师范大学生命与地理科学学院青海省自然地理与环境过程重点实验室/青藏高原环境与资源教育部重点实验室, 西宁 810008;
    2哈尔滨工程大学航天与建筑工程学院, 哈尔滨 150001
  • 收稿日期:2015-12-02 发布日期:2016-06-18
  • 通讯作者: xiaohonggao226@163.com
  • 作者简介:杨灵玉,女,1990年生,硕士研究生. 主要从事遥感应用与地理数据空间分析研究. E-mail: yang_lingyu@126.com
  • 基金资助:
    本文由青海省科技厅自然科学基金项目(2011-Z-903)、青海师范大学创新基金项目(QS2012-08)、青海省重点实验室发展专项(2014-Z-Y24,2015-Z-Y01)资助

Estimating heavy metal concentrations in topsoil from vegetation reflectance spectra of Hyperion images: A case study of Yushu County, Qinghai, China.

YANG Ling-yu1, GAO Xiao-hong1*, ZHANG Wei1,2, SHI Fei-fei1, HE Lin-hua1, JIA Wei1   

  1. 1Qinghai Province Key Laboratory of Physical Geography and Environmental Process/Ministry of Education Key Laboratory on Environments and Resources in Qinghai-Tibet Plateau, School of Life and Geographical Science, Qinghai Normal University, Xining 810008, China;
    2College of Astronautics and Civil Engineering, Harbin Engineering University, Harbin 150001, China
  • Received:2015-12-02 Published:2016-06-18

摘要: 本研究主要探讨了利用Hyperion影像植被光谱估算土壤重金属含量的可行性.以野外采集的三江源区玉树县48个表层土壤样品As、Pb、Zn、Cd实验室测定含量值,以及从两景Hyperion影像提取的48个土壤样本点相应的176个植被光谱反射率波段及构建的5种植被指数为数据源,利用偏最小二乘回归方法(PLSR)建立土壤各重金属含量与上述两套Hyperion影像上提取的变量之间的估算模型.模型分别为176个植被光谱反射率波段与土壤各重金属含量间的估算模型(植被光谱反射率模型),和以5种植被指数作为自变量,与土壤各重金属含量建立的估算模型(综合植被指数模型).运用验证样本的4种重金属元素实测含量值的标准差与均方根误差的比值(RPD)作为检验标准,As、Pb两种模型RPD均小于1.4,不具备粗略估算能力;Zn、Cd两种模型RPD分别为1.53、1.46与1.46、1.42,均具备粗略估算能力.根据上述结果将Zn的光谱反射率估算模型与Hyperion影像相结合反演得到土壤重金属Zn含量的空间分布,Zn含量在214国道、308省道和乡镇附近偏高,主要受到较强的人类活动影响.表明运用Hyperion高光谱影像植被光谱反射率可以间接估算土壤Zn、Cd元素含量.

Abstract: In this study, we explored the feasibility of estimating the soil heavy metal concentrations using the hyperspectral satellite image. The concentration of As, Pb, Zn and Cd elements in 48 topsoil samples collected from the field in Yushu County of the Sanjiangyuan regions was measured in the laboratory. We then extracted 176 vegetation spectral reflectance bands of 48 soil samples as well as five vegetation indices from two Hyperion images. Following that, the partial least squares regression (PLSR) method was employed to estimate the soil heavy metal concentrations using the above two independent sets of Hyperion-derived variables, separately constructed the estimation model between the 176 vegetation spectral reflectance bands and the soil heavy metal concentrations (called the vegetation spectral reflectance-based estimation model), and between the five vegetation indices being used as the independent variable and the soil heavy metal concentrations (called synthetic vegetation index-based estimation model). Using RPD (the ratio of standard deviation from the 4 heavy metals measured values of the validation samples to RMSE) as the validation criteria, the RPDs of As and Pb concentrations from the two models were both less than 1.4, which suggested that both models were incapable of roughly estimating As and Pb concentrations; whereas the RPDs of Zn and Cd were 1.53, 1.46 and 1.46, 1.42, respectively, which implied that both models had the ability for rough estimation of Zn and Cd concentrations. Based on those results, the vegetation spectral-based estimation model was selected to obtain the spatial distribution map of Zn concentration in combination with the Hyperion image. The estimated Zn map showed that the zones with high Zn concentrations were distributed near the provincial road 308, national road 214 and towns, which could be influenced by human activities. Our study proved that the spectral reflectance of Hyperion image was useful in estimating the soil concentrations of Zn and Cd.