1 Exploiting Multisensor Spectral Data to Improve Crop Residue Cover Estimates for Management of Agricultural Water Quality Magda S. Galloza 1, Melba M.

Slides:



Advertisements
Similar presentations
Lab for Remote Sensing Hydrology and Spatial Modeling Dept. of Bioenvironmental Systems Engineering, NTU Satellite Remote Sensing for Land-Use/Land-Cover.
Advertisements

Beyond Spectral and Spatial data: Exploring other domains of information GEOG3010 Remote Sensing and Image Processing Lewis RSU.
Comparison between the United States Soil Conservation Service (SCS) curve number, the Pitman and Monarch models for estimating rainfall-runoff in South-Eastern.
1 Manifold Alignment for Multitemporal Hyperspectral Image Classification H. Lexie Yang 1, Melba M. Crawford 2 School of Civil Engineering, Purdue University.
Laboratory for Applications of Remote Sensing Critical Class Oriented Active Learning for Hyperspectral Image Classification Hyperspectral Image Classification.
Walloon Agricultural Research Centre Extending Crop Growth Monitoring System (CGMS) for mapping drought stress at regional scale D. Buffet, R. Oger Walloon.
Phosphorus Indices: an Understanding of Upper Mississippi Strategies John A. Lory, Ph.D. Division of Plant Sciences University of Missouri.
Predicting and mapping biomass using remote sensing and GIS techniques; a case of sugarcane in Mumias Kenya Odhiambo J.O, Wayumba G, Inima A, Omuto C.T,
On Remotely Sensed Responses Monitoring Science and Technology Symposium September 21, 2004 Raymond L. Czaplewski, Ph.D. USDA Forest Service Rocky Mountain.
Introduction The agricultural practice of field tillage has dramatic effects on surface hydrologic properties, significantly altering the processes of.
EFFECT OF SELECT YIELD IMPROVEMENT PROJECTS ON POTATO YIELDS “NB Potato Industry Transformation Initiative”
Investigation of Seasonal Hydrology and Variable Source Areas within Regions of Ontario Ramesh Rudra (R.P. Rudra, B. Gharabaghi, S, Gregori, W.T. Dickinson)
Liang APEIS Capacity Building Workshop on Integrated Environmental Monitoring of Asia-Pacific Region September 2002, Beijing,, China Atmospheric.
Estimating forest structure in wetlands using multitemporal SAR by Philip A. Townsend Neal Simpson ES 5053 Final Project.
Remote Sensing Hyperspectral Imaging AUTO3160 – Optics Staffan Järn.
Application Of Remote Sensing & GIS for Effective Agricultural Management By Dr Jibanananda Roy Consultant, SkyMap Global.
Remote Sensing of Aphid-Induced Stress in Wheat BAE/SOIL Precision Agriculture Oklahoma State University Victor W. Slowik April 20, 2001.
Soil Moisture Estimation Using Hyperspectral SWIR Imagery Poster Number IN43B-1184 D. Lewis, Institute for Technology Development, Building 1103, Suite.
Multiple Criteria for Evaluating Land Cover Classification Algorithms Summary of a paper by R.S. DeFries and Jonathan Cheung-Wai Chan April, 2000 Remote.
Characterizing Soil Erosion in Albania using Remote Sensing Ryan L. Perroy Geography Department University of California, Santa Barbara.
Impact of Climate Change on Flow in the Upper Mississippi River Basin
Remote Sensing of Drought Lecture 9. What is drought? Drought is a normal, recurrent feature of climate. It occurs almost everywhere, although its features.
Module 2.1 Monitoring activity data for forests using remote sensing REDD+ training materials by GOFC-GOLD, Wageningen University, World Bank FCPF 1 Module.
NUE Workshop: Improving NUE using Crop Sensing, Waseca, MN
Remote Sensing Hyperspectral Remote Sensing. 1. Hyperspectral Remote Sensing ► Collects image data in many narrow contiguous spectral bands through the.
TAILING MODELLED AND MEASURED SPECTRUM FOR MINE TAILING MAPPING IN TUNISIAN SEMI-ARID CONTEXT N. Mezned 1,2, S. Abdeljaouad 1, M. R. Boussema
The University of Mississippi Geoinformatics Center NASA RPC – March, Evaluation for the Integration of a Virtual Evapotranspiration Sensor Based.
U.S. Department of the Interior U.S. Geological Survey Assessment of Conifer Health in Grand County, Colorado using Remotely Sensed Imagery Chris Cole.
Satellite Cross comparisonMorisette 1 Satellite LAI Cross Comparison Jeff Morisette, Jeff Privette – MODLAND Validation Eric Vermote – MODIS Surface Reflectance.
Operational Agriculture Monitoring System Using Remote Sensing Pei Zhiyuan Center for Remote Sensing Applacation, Ministry of Agriculture, China.
U.S. Department of the Interior U.S. Geological Survey Geometric Assessment of Remote Sensed Data Oct Presented By: Michael Choate, SAIC U.S.
Resolution A sensor's various resolutions are very important characteristics. These resolution categories include: spatial spectral temporal radiometric.
Slide #1 Emerging Remote Sensing Data, Systems, and Tools to Support PEM Applications for Resource Management Olaf Niemann Department of Geography University.
PREFER 1 st Annual Review Meeting, 5-6 Dec 2013, Milano-Italy PREFER WP 3.2 Information support to Recovery/Reconstruction Task 7 Damage Severity Map PREFER.
Abstract: Dryland river basins frequently support both irrigated agriculture and riparian vegetation and remote sensing methods are needed to monitor.
Remote Sensing. Vulnerability is the degree to which a system is susceptible to, or unable to cope with, adverse effects of climate change, including.
PREFER 1 st Annual Review Meeting, 5-6 Dec 2013, Milano-Italy PREFER WP 3.2, Task 7.
Canada Centre for Remote Sensing Field measurements and remote sensing-derived maps of vegetation around two arctic communities in Nunavut F. Zhou, W.
Snow Properties Relation to Runoff
Application of Neuro-Fuzzy Techniques to Predict Ground Water Vulnerability B. Dixon, Ph.D. University of South Florida St. Petersburg, Florida 33701,
Introduction Conservation of water is essential to successful dryland farming in the Palouse region. The Palouse is under the combined stresses of scarcity.
Spectral unmixing of vegetation, soil and dry carbon cover in arid regions: comparing multispectral and hyperspectral observations G.P.Asner and K.B.Heidebrecht.
Mirza Muhammad Waqar HYPERSPECTRAL REMOTE SENSING - SENSORS 1 Contact:
14 ARM Science Team Meeting, Albuquerque, NM, March 21-26, 2004 Canada Centre for Remote Sensing - Centre canadien de télédétection Geomatics Canada Natural.
H. Lexie Yang1, Dr. Melba M. Crawford2
Development of Vegetation Indices as Economic Thresholds for Control of Defoliating Insects of Soybean James BoardVijay MakaRandy PriceDina KnightMatthew.
The University of Mississippi Geoinformatics Center NASA MRC RPC – 11 July 2007 Evaluating the Integration of a Virtual ET Sensor into AnnGNPS Model Rapid.
Hyperspectral remote sensing
October 12, 2015 Iowa State University Indrajeet Chaubey Purdue University Water Quality.
WATER BALANCE MODEL TO PREDICT CLIMATE CHANGE IMPACTS IN THE WATERSHED EPITÁCIO PESSOA DAM– PARAÍBA RIVER - BRAZIL Dra. Josiclêda D. Galvíncio Dra. Magna.
IGARSS 2011, Jul. 27, Vancouver 1 Monitoring Vegetation Water Content by Using Optical Vegetation Index and Microwave Vegetation Index: Field Experiment.
Hyperspectral Remote Sensing Ruiliang Pu Center for Assessment and Monitoring of Forest and Environmental Resources Department of Environmental Science,
Beyond Spectral and Spatial data: Exploring other domains of information: 3 GEOG3010 Remote Sensing and Image Processing Lewis RSU.
2011 IEEE International Geoscience and Remote Sensing Symposium (IGARSS) Aihua Li Yanchen Bo
A Remote Sensing Approach for Estimating Regional Scale Surface Moisture Luke J. Marzen Associate Professor of Geography Auburn University Co-Director.
Land Cover Classification and Monitoring Case Studies: Twin Cities Metropolitan Area –Multi-temporal Landsat Image Classification and Change Analysis –Impervious.
Environmental Modeling Weighting GIS Layers Weighting GIS Layers.
LANDSAT EVALUATION OF TRUMPETER SWAN (CYGNUS BUCCINATOR) HISTORICAL NESTING SITES IN YELLOWSTONE NATIONAL PARK Laura Cockrell and Dr. Robert B. Frederick.
Orbits and Sensors Multispectral Sensors. Satellite Orbits Orbital parameters can be tuned to produce particular, useful orbits Geostationary Sun synchronous.
Using vegetation indices (NDVI) to study vegetation
Term Project Presentation
Hyperspectral Sensing – Imaging Spectroscopy
Overview of Joint Agency Commercial Imagery Evaluation (JACIE)
HIERARCHICAL CLASSIFICATION OF DIFFERENT CROPS USING
Hyperspectral Remote Sensing
REMOTE SENSING Multispectral Image Classification
Hyperspectral remote sensing ('Image spectroscopy')
Planning a Remote Sensing Project
Summary - end of term Lab Monday: 4 April return of assignments Lecture exam: 5 April, projects by end of term: April 6 Lecture evaluation.
Igor Appel Alexander Kokhanovsky
Presentation transcript:

1 Exploiting Multisensor Spectral Data to Improve Crop Residue Cover Estimates for Management of Agricultural Water Quality Magda S. Galloza 1, Melba M. Crawford 2 School of Civil Engineering, Purdue University and Laboratory for Applications of Remote Sensing {mgalloza 1, mcrawford 2 July 28, 2011 IEEE International Geoscience and Remote Sensing Symposium

2 Outline Introduction −Estimation of crop residue Research Motivation −Evaluation of Hyperspectral / Multispectral Sensor data for estimating residue cover −Investigation of approaches for large scale applications Methodology Experimental Results Summary and Future Directions

3 Ecosystem-based management approaches (monitoring and damage assessments) Introduction Residue Cover (RC): Plant material remaining in field after grain harvest and possible tillage - Nutrients - Organic material (soil) - Agricultural ecosystem stability - water evaporation - water infiltration - moderate soil temperature - Critical in sustaining soil quality - erosion - runoff rates

4 Introduction Manual methods of analysis −Statistical sampling of fields via windshield surveys  Costly, requires trained personnel −Line transect method  Time and labor intensive Remote sensing based approaches −Capability for 100% sampling −Detect within field variability −GREATER coverage area −Potentially reduce subjective errors Satellite Track Landsat-7 ETM+ 185 Km EO-1 Hyperion 7.5 Km EO-1 ALI 37 Km

5 Research Motivation Transect Method vs. Remote Sensing based Method 66 ft 100 beads

6 Research Motivation Land Cover Characteristics −Agricultural Cover Discrimination and Assessment

7 Research Motivation Evaluate performance of multispectral and hyperspectral data for estimating residue cover over local and extended areas Evaluate performance of next generation sensors Landsat 8 Operational Land Imager (OLI) Investigate sensor fusion scenarios Potential contribution of hyperspectral data for improving (calibrating) residue cover estimates derived from wide coverage multispectral data Contributions of multisensor fusion

8 Band based indicesBand based indices −Based on the absorption characteristics (reflectance) of RC −Linear relationship between RC and indices exploited via regression models Multispectral NDTIMultispectral NDTI (Normalized Difference Tillage Index) −Empirical models developed and validated locally −Applicable to multiple sensors: ASTER, Landsat, ALI (EO-1) −Sensitive to soil characteristics Approach - NDTI Band EO-I (ALI) Spectral Range (µm) Bandwidth (nm) GSD (m) Pan B1p B B B B B4p B5p B B Band L7 ETM+ Wavelength (nm) Bandwidth (nm) GSD (m) Pan B B B B B B B Where: - TM7: Landsat TM band 7 or equivalent - TM5: Landsat TM band 5 or equivalent NDTI = (TM5 - TM7)/(TM5 + TM7)

9 Proposed Approaches - CAI Hyperspectral CAI -Hyperspectral CAI - (Cellulose Absorption Index) −Related to the depth of the absorption feature (2100 nm) −Demonstrated to accurately detect estimate RC [Daughtry, 2008] −Robust to crop and soil types characteristics −Limited coverage and availability Where: - R2.0, R2.1, R2.2: average response of 3 bands centered at 2000 nm, 2100 nm and 2200 nm respectively CAI = 0.5 * (R2.0 + R2.2) – R2.1 Estimate of the depth of the cellulose absorption feature

10 Study Location / Field Data

11 Remote Sensing Data ( ) Data Available Spring 2008 Fall 2008 Spring 2009 Fall 2009 Spring 2010 Fall 2010 EO-1 ALI/HyperionMay 6Nov 1No DataOct 11May 23Nov 2 Landsat TMJune 11Nov 2May 29Oct 20April 22Nov 8 SpecTIR AirborneNo Data Nov 3June 5No DataMay 24No Data Satellite Track Landsat-7 ETM+ 185 Km EO-1 Hyperion 7.5 Km EO-1 ALI 37 Km

12 Linear Models Substitute in Model

13 Model 1 - CAI Index Field Residue Cover (%) Total Area SpecTIR 4m (hec) SpecTIR 30m (hec) Hyperion (hec) 0% - 25% % - 50% % - 75% % - 100% Watershed Scale Evaluation SpecTIR (4m) EO-1 Hyperion (30m) SpecTIR (30m) Field Residue Cover (%) Residue Coverage SpecTIR 4m (hec) SpecTIR 30m (hec) Hyperion 30m (hec) 0% - 25% % - 50% % - 75% % - 100% % - 25% 26% - 50% 51% - 75% 76% - 100% Resample

14 Model 2 – NDTI Index Residue Cover (%) Total Area Landsat (hec) ALI (hec) SpecTIR 4m (hec) 0% - 25% % - 50% % - 75% % - 100% Model 2 - ALI Watershed Scale Evaluation Model 2 – Landsat TM Model 1 – SpecTIR (4m) Residue Cover (%) Residue Coverage Landsat (hec) ALI (hec) SpecTIR 4m (hec) 0% - 25% % - 50% % - 75% % - 100% % - 25% 26% - 50% 51% - 75% 76% - 100%

15 Residue Cover (%) Landsat Difference (hec) ALI Difference (hec) -85% - -80% % - -60% % - -40% % - -20% % - 0% % - 20% % - 40% % - 60% CAI (SpecTIR) vs. NDTI (Landsat/ALI) SpecTIR vs. Landsat TM SpecTIR vs. ALI -85% - -80% -70% - -60% -59% - -40% -39% - -20% -19% - 0% 1% - 20% 21% - 40% 41% - 60%

16 Little Pine Creek Model Applied to Darlington Region Residue Cover (%) ALI (hec) ACRE Model (hec) 0% - 25% % - 50% % - 75% % - 100% Watershed Scale Evaluation Little Pine Creek Data Darlington Data (ALI) Model 2 0% - 25% 26% - 50% 51% - 75% 76% - 100%

17 Little Pine Creek Model Applied to Darlington Region Residue Cover (%) SpecTIR (hec) ACRE Model (hec) 0% - 25% % - 50% % - 75% % - 100% Watershed Scale Evaluation Little Pine Creek Data (Model 1) Darlington Data (SpecTIR) Model 1 0% - 25% 26% - 50% 51% - 75% 76% - 100%

18 Model 3 – Substitution in Model 1 Residue Cover (%) Model 3 (hec) SpecTIR (hec) 0% - 25% % - 50% % - 75% % - 100% Model 3 - (Substitution Model) Watershed Scale Evaluation Model 2 – SpecTIR (30m) Substitute in Model 1 0% - 25% 26% - 50% 51% - 75% 76% - 100%

19 Multispectral – not sensitive enough to the low coverage Potential improvement from next Landsat generation ALI multispectral sensor provides better residue cover estimates in comparison with Landsat TM Future Directions Weighted least squares method for multisensor fusion Effect of soil moisture Assimilate RC information into a hydrologic model -Pushbroom vs. whiskbroom -Radiometrically ALI – 12-bit (vs. 8 bit) -ALI SNR between four and ten times larger than SNR for TM - Operational Land Imager (OLI) on the Landsat Follow- on Mission - will be similar to the ALI sensor Conclusions and Future Work - The OLI design features a multispectral imager with pushbroom architecture of ALI heritage

20 Thank You This research is supported by the U.S. Department of Agriculture, the Agricultural Research Service, the Department of Agronomy and its Laboratory and the Laboratory for Applications of Remote Sensing (LARS) at Purdue University.

21 SpecTIR 30m vs. Hyperion 30m Residue Cover (%) Difference (hec) -60% - -40% % - -20% % - 0% % - 20% % - 40% % - 60% % - 70% % - -40% -39% - -20% -19% - 0% 1% - 20% 21% - 40% 41% - 60% 61% - 70%