Derivation of 16-day time-series NDVI data for environmental studies using a data assimilation approach

Many ecological and environmental applications require time-series data, which are collected with spatial extent from local, regional or continental levels and granularity ranging from fine to coarse spatial resolution. These types of data can be too difficult to collect using typical field surveys, but they can be derived using remote-sensing images and image-processing technologies. The common time-series normalized difference vegetation index (NDVI) data are AVHRR-derived at spatial resolutions of 1 or 8 km, MODIS-derived at 250 m, 500 m, 1 km or 8 km resolutions, and SPOT-VGT imagery at 1 km resolution. Landsat imagery-derived time-series NDVI data are often unavailable for many areas due to the difficulty of acquiring cloud-free images given the temporally infrequent coverage of this sensor. For this study, we used a closest-spectral-fit concept as the basis for a data mining model and developed a data assimilation model in order to derive 16-day time-series NDVI data. In a multidimensional spectral space, if pixel i has the closest reflectance values to pixel j, pixel i is called the closest-spectral-fit of pixel j, and pixels i and j are called closest-spectral-fit pixels. Fifteen Landsat TM images covering northern Michigan were acquired from 22 March 2010 to 1 November 2010, in a 16-day cycle. A cloud-free image is used as the reference image to predict NDVI images for the other 14 dates. The forecasted NDVI data explain 80% variation in the observed NDVI. TM band 4 is forecasted at the same performance level as NDVI, and forecasts of bands 3 and 2 are relatively highly correlated with the forecasts of observed bands. The closest-spectral-fit data assimilation method has the capability to produce historical NDVI data at finer spatial resolution as far back as 1972, which broaden and enhance potential applications to the modeling of environmental and ecological patterns and processes.

[1]  H. Poulos Mapping fuels in the Chihuahuan Desert borderlands using remote sensing, geographic information systems, and biophysical modeling , 2009 .

[2]  Jesslyn F. Brown,et al.  Measuring phenological variability from satellite imagery , 1994 .

[3]  N. Pettorelli,et al.  Using the satellite-derived NDVI to assess ecological responses to environmental change. , 2005, Trends in ecology & evolution.

[4]  K. McGwire,et al.  Patterns of floristic richness in vegetation communities of California: regional scale analysis with multi-temporal NDVI , 2004 .

[5]  H. Nagendra Using remote sensing to assess biodiversity , 2001 .

[6]  Soizik Laguette,et al.  Remote sensing applications for precision agriculture: A learning community approach , 2003 .

[7]  William F. Laurance,et al.  Influence of landscape heterogeneity on spatial patterns of wood productivity, wood specific density and above ground biomass in Amazonia , 2009 .

[8]  Siamak Khorram,et al.  Regional Scale Land Cover Characterization Using MODIS-NDVI 250 m Multi-Temporal Imagery: A Phenology-Based Approach , 2006 .

[9]  Stuart E. Marsh,et al.  Multi-sensor NDVI data continuity: Uncertainties and implications for vegetation monitoring applications , 2006 .

[10]  J. Paruelo,et al.  Biozones: vegetation units defined by functional characters identifiable with the aid of satellite sensor images , 1992 .

[11]  Seiji Hayashi,et al.  Using NOAA AVHRR Data to Assess Flood Damage in China , 2003, Environmental monitoring and assessment.

[12]  C. Cieszewski,et al.  Spatial regression modeling of tree height- diameter relationships , 2009 .

[13]  O. Sala,et al.  Current Distribution of Ecosystem Functional Types in Temperate South America , 2001, Ecosystems.

[14]  M. Katz Validation of models , 2006 .

[15]  Allen H Hurlbert,et al.  The Effect of Energy and Seasonality on Avian Species Richness and Community Composition , 2002, The American Naturalist.

[16]  Simon A. Levin,et al.  Challenges in the development of a theory of community and ecosystem structure and function , 1989 .

[17]  J. Wiens Spatial Scaling in Ecology , 1989 .

[18]  F. Maselli Use of NOAA-AVHRR NDVI images for the estimation of dynamic fire risk in Mediterranean areas , 2003 .

[19]  R. Houghton,et al.  Aboveground Forest Biomass and the Global Carbon Balance , 2005 .

[20]  M. Madden,et al.  Large area forest inventory using Landsat ETM+: A geostatistical approach , 2009 .

[21]  C. Field,et al.  A reanalysis using improved leaf models and a new canopy integration scheme , 1992 .

[22]  Limin Yang,et al.  An analysis of relationships among climate forcing and time-integrated NDVI of grasslands over the U.S. northern and central Great Plains , 1998 .

[23]  C. Tucker,et al.  Increased plant growth in the northern high latitudes from 1981 to 1991 , 1997, Nature.

[24]  A. Møller,et al.  Analysis and Interpretation of Long-Term Studies Investigating Responses to Climate Change , 2004 .

[25]  G. Asrar,et al.  Estimating Absorbed Photosynthetic Radiation and Leaf Area Index from Spectral Reflectance in Wheat1 , 1984 .

[26]  J. Ledolter,et al.  Introduction to Regression Modeling , 2005 .

[27]  C. Tucker,et al.  Climate-Driven Increases in Global Terrestrial Net Primary Production from 1982 to 1999 , 2003, Science.

[28]  D. Roy,et al.  Multi-temporal MODIS-Landsat data fusion for relative radiometric normalization, gap filling, and prediction of Landsat data , 2008 .

[29]  W. Dong,et al.  The influence of vegetation cover on summer precipitation in China: A statistical analysis of NDVI and climate data , 2003 .

[30]  Marguerite Madden,et al.  Closest Spectral Fit for Removing Clouds and Cloud Shadows , 2009 .

[31]  Marguerite Madden,et al.  A linear mixed-effects model of biomass and volume of trees using Landsat ETM+ images , 2007 .

[32]  W. C. Clark,et al.  Scales of climate impacts , 1985 .