Deriving the Characteristic Scale for Effectively Monitoring Heavy Metal Stress in Rice by Assimilation of GF-1 Data with the WOFOST Model

Accurate monitoring of heavy metal stress in crops is of great importance to assure agricultural productivity and food security, and remote sensing is an effective tool to address this problem. However, given that Earth observation instruments provide data at multiple scales, the choice of scale for use in such monitoring is challenging. This study focused on identifying the characteristic scale for effectively monitoring heavy metal stress in rice using the dry weight of roots (WRT) as the representative characteristic, which was obtained by assimilation of GF-1 data with the World Food Studies (WOFOST) model. We explored and quantified the effect of the important state variable LAI (leaf area index) at various spatial scales on the simulated rice WRT to find the critical scale for heavy metal stress monitoring using the statistical characteristics. Furthermore, a ratio analysis based on the varied heavy metal stress levels was conducted to identify the characteristic scale. Results indicated that the critical threshold for investigating the rice WRT in monitoring studies of heavy metal stress was larger than 64 m but smaller than 256 m. This finding represents a useful guideline for choosing the most appropriate imagery.

[1]  Riccardo Poli,et al.  Particle swarm optimization , 1995, Swarm Intelligence.

[2]  Fumin Wang,et al.  New Vegetation Index and Its Application in Estimating Leaf Area Index of Rice , 2007 .

[3]  Anne Puissant,et al.  Optimizing Spatial Resolution of Imagery for Urban Form Detection - The Cases of France and Vietnam , 2011, Remote. Sens..

[4]  Ting Li,et al.  Estimating regional heavy metal concentrations in rice by scaling up a field-scale heavy metal assessment model , 2012, Int. J. Appl. Earth Obs. Geoinformation.

[5]  Xuezheng Shi,et al.  Hyper-spectral remote sensing to monitor vegetation stress , 2008 .

[6]  Conceição Santos,et al.  Cadmium toxicity affects photosynthesis and plant growth at different levels , 2012, Acta Physiologiae Plantarum.

[7]  C. A. van Diepen,et al.  User's guide for the WOFOST 7.1 crop growth simulation model and WOFOST Control Center 1.5. , 1998 .

[8]  Xingmei Liu,et al.  The identification of 'hotspots' of heavy metal pollution in soil-rice systems at a regional scale in eastern China. , 2014, The Science of the total environment.

[9]  Stuart R. Phinn,et al.  Optimizing Remotely Sensed Solutions for Monitoring, Modeling, and Managing Coastal Environments , 2000 .

[10]  Peter M. Atkinson,et al.  Selecting the spatial resolution of airborne MSS imagery for small-scale agricultural mapping , 1997 .

[11]  R. Waring,et al.  The normalized difference vegetation index of small Douglas-fir canopies with varying chlorophyll concentrations , 1994 .

[12]  Zhongxin Chen,et al.  Monitoring plant response to phenanthrene using the red edge of canopy hyperspectral reflectance. , 2014, Marine pollution bulletin.

[13]  G. Chibuike,et al.  Heavy Metal Polluted Soils: Effect on Plants and Bioremediation Methods , 2014 .

[14]  Qingbin Song,et al.  Environmental effects of heavy metals derived from the e-waste recycling activities in China: a systematic review. , 2014, Waste management.

[15]  S. M. Jong,et al.  Optimizing spatial image support for quantitative mapping of natural vegetation , 2009 .

[16]  Frédéric Baret,et al.  Multivariate quantification of landscape spatial heterogeneity using variogram models , 2008 .

[17]  G. Hay,et al.  Remote Sensing Contributions to the Scale Issue , 1999 .

[18]  Xu Jia,et al.  Advances in the Study Uptake and Accumulation of Heavy Metal in Rice (Oryza sativa) and its Mechanisms , 2005 .

[19]  Fabian Löw,et al.  Defining the Spatial Resolution Requirements for Crop Identification Using Optical Remote Sensing , 2014, Remote. Sens..

[20]  Raksha Singh,et al.  Understanding the responses of rice to environmental stress using proteomics. , 2013, Journal of proteome research.

[21]  Kunquan Li,et al.  Interaction of Cd and five mineral nutrients for uptake and accumulation in different rice cultivars and genotypes , 2003 .

[22]  R. Fournier,et al.  Remote sensing and the measurement of geographical entities in a forested environment. 2. The optimal spatial resolution , 1994 .

[23]  Yuhong He,et al.  Studying mixed grassland ecosystems II: optimum pixel size , 2006 .

[24]  Kang Li Accumulation of Cu as Single and Complex Pollutants in Rice , 2003 .

[25]  F. Baret,et al.  Influence of landscape spatial heterogeneity on the non-linear estimation of leaf area index from moderate spatial resolution remote sensing data , 2006 .

[26]  P. Das,et al.  Studies on cadmium toxicity in plants: a review. , 1997, Environmental pollution.

[27]  Dale A. Quattrochi,et al.  Spatial and temporal scaling of thermal infrared remote sensing data , 1995 .

[28]  Eric D. Kolaczyk,et al.  On the choice of spatial and categorical scale in remote sensing land cover classification , 2005 .

[29]  Zhao-Liang Li,et al.  Scale Issues in Remote Sensing: A Review on Analysis, Processing and Modeling , 2009, Sensors.

[30]  Dale A. Quattrochi,et al.  The Need for a Lexicon of Scale Terms in Integrating Remote Sensing Data with Geographic Information Systems , 1993 .

[31]  P. J. Curran,et al.  Selecting a spatial resolution for estimation of per-field green leaf area index , 1988 .

[32]  Meiling Liu,et al.  An improved assimilation method with stress factors incorporated in the WOFOST model for the efficient assessment of heavy metal stress levels in rice , 2015, Int. J. Appl. Earth Obs. Geoinformation.

[33]  Qinghua Zhang,et al.  High levels of heavy metals in rice (Oryza sativa L.) from a typical E-waste recycling area in southeast China and its potential risk to human health. , 2008, Chemosphere.

[34]  C. Woodcock,et al.  The factor of scale in remote sensing , 1987 .

[35]  Feng Liu,et al.  The Dynamic Assessment Model for Monitoring Cadmium Stress Levels in Rice Based on the Assimilation of Remote Sensing and the WOFOST Model , 2015, IEEE Journal of Selected Topics in Applied Earth Observations and Remote Sensing.

[36]  H. Hyppänen,et al.  Spatial autocorrelation and optimal spatial resolution of optical remote sensing data in boreal forest environment , 1996 .

[37]  Peter M. Atkinson,et al.  Choosing an appropriate spatial resolution for remote sensing investigations , 1997 .

[38]  Pierre Defourny,et al.  A conceptual framework to define the spatial resolution requirements for agricultural monitoring using remote sensing , 2010 .

[39]  D. Sims,et al.  Optimum pixel size for hyperspectral studies of ecosystem function in southern California chaparral and grassland , 2003 .

[40]  Mui Lay,et al.  Reflectance properties and physiological responses of Salicornia virginica to heavy metal and petroleum contamination. , 2005, Environmental pollution.

[41]  Hong-Seog Park,et al.  Effects of heavy metals on antioxidants and stress-responsive gene expression in Javanese medaka (Oryzias javanicus). , 2009, Comparative biochemistry and physiology. Toxicology & pharmacology : CBP.

[42]  Kenneth C. McGwire,et al.  Spatial structure, sampling design and scale in remotely-sensed imagery of a California savanna woodland , 1993 .

[43]  N. Lam,et al.  On the Issues of Scale, Resolution, and Fractal Analysis in the Mapping Sciences* , 1992 .

[44]  Zhang Jun-hui,et al.  Eco-toxicity and metal contamination of paddy soil in an e-wastes recycling area. , 2009, Journal of hazardous materials.

[45]  Peter M. Atkinson,et al.  Defining an optimal size of support for remote sensing investigations , 1995, IEEE Trans. Geosci. Remote. Sens..

[46]  Salahuddin,et al.  Cadmium-induced functional and ultrastructural alterations in roots of two transgenic cotton cultivars. , 2009, Journal of hazardous materials.