1 / 55

By Aarthy Sabesan GIS Research Lab

Geo-Spatial Assessment of the Impact of Land Cover Dynamics and the Distribution of Land Resources on Soil and Water Quality in the Santa Fe River Watershed. By Aarthy Sabesan GIS Research Lab. Located in north-central Florida Mixed land use watershed covering 3,585 km 2

ralph
Télécharger la présentation

By Aarthy Sabesan GIS Research Lab

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Geo-Spatial Assessment of the Impact of Land Cover Dynamics and the Distribution of Land Resources on Soil and Water Quality in the Santa Fe River Watershed By Aarthy Sabesan GIS Research Lab

  2. Located in north-central Florida • Mixed land use watershed covering 3,585 km2 • Encompasses parts of Suwannee, Gilchrist, Columbia, Union, Bradford, Alachua, Baker and Clay • Administratively, Suwannee River Water Management District (SRWMD)

  3. 1995 Land Use / Land Cover (LULC) classes

  4. Soil Orders

  5. Environmental Geology

  6. DRASTIC Index Depth to water Net recharge Aquifer media Soil media Topography Impact of the vadose zone Hydraulic conductivity

  7. Non-point source pollutants are the major source of surface and ground water pollution in U.S today. • Increasing concentrations of nitrate-nitrogen are observed in the surface water, ground water and springs in the SRWMD. • Contribution of the SFRW has increased by 4% from 2001 to 2002. • 2002, the Suwannee River Basin: 2,971 tons nitrate-nitrogen. • SFRW (5.7% of the Suwannee River Basin): 19.6% of the N loads.

  8. Hypotheses • Spatially distributed patterns of land resources and land cover dynamics are useful proxies providing information about nitrogen levels in soils and surface water • Land use / land cover (LULC) and soils are the major factors impacting soil and water nitrogen in the SFRW

  9. Characterize the land cover dynamics in the SFRW from 1990 to present • Quantify the spatial distribution of soil nitrate-nitrogen across the SFRW • Investigate the spatial relationships between watershed characteristics and soil and water quality

  10. Module 1 Land cover dynamics in the SFRW

  11. Objective • Identify recent changes within land cover classes • Quantify the areal extent of these changes • Assess the trend or nature of change within land cover classes

  12. Band Wavelength (µm) Spectral location 1 0.45-0.52 Blue 2 0.52-0.60 Green 3 0.63-0.69 Red 4 0.76-0.90 Near-infrared 5 1.55-1.75 Mid-infrared 6 10.4-12.5 Thermal infrared 7 2.08-2.35 Mid-infrared Materials • Landsat Satellite Series • NASA and Dept. of Interior • Spatial resolution – 30m

  13. Landsat TM • August 26th 1990 • August 13th 2000 • Landsat ETM+ • February 11th 2003 Path 17, Row 39

  14. Methods • Design of a land cover classification scheme • Ground truth data collection • Image processing • Change trajectory analysis

  15. Design of a Land Cover Classification Scheme • Four levels of land use / land cover classification • Aggregation of level 2, 3 and 4 to create level 1 • Land cover classes used for the analysis Coniferous pine, Upland forest, Agriculture, Rangeland,Urban,Wetland,Water

  16. Ground Truth Data Collection • 487 Ground Control Points (GCP’s) • Categorization into training and accuracy assessment sites (60% / 40%)

  17. Preprocessing Image Processing • Geometric correction • Atmospheric correction • Noise removal • Pre-classification scene stratification • Image classification (Supervised approach) • Accuracy assessment

  18. Correction for distortions in platform attributes Preprocessing:Geometric Correction 2000 Landsat image imposed over the 2003 image RMS error: 0.5 pixel

  19. To account for atmospheric attenuation factors Preprocessing:Atmospheric Correction Dark object subtraction technique Based on the assumption that the reflectance from water bodies is close to zero. RDOSN = R * (RDO )/ ((Cos (90-θ)*)/180)

  20. Raw Landsat image Splitting the image into individual bands Identifying a dark object, like a water body Pixel value of the dark object in the particular band Header file Pixel value of the dark object in the particular band Θ values RDOSN = R * (RDO )/ ((Cos (90-θ)*Π)/180) RDOSM = R * (RDO )/ ((Cos (90-θ)*Π)/180) RDOSN RDOSM Layer stacking the individually calibrated bands Atmospherically corrected Landsat image.

  21. Preprocessing: Noise Removal Masking cloud and cloud shadow Cloud / cloud shadow infested image Cloud / cloud shadow mask Cloud / cloud shadow masked image of SFRW

  22. Pre-Classification Scene Stratification To separate spectrally similar classes of urban, agriculture and rangeland

  23. Image Classification

  24. Image Classification: Training Stage • Numerical descriptors of land cover classes • Two sets of spectral signatures were developed Winter scene Summer scene

  25. Minimum Distance to Mean Classifier (MDM) Image Classification: Classification Stage

  26. 2000 1990 Image Classification: Output Stage

  27. 2003 Image Classification: Output Stage Overall classification accuracy: 82%

  28. Three data change image of land cover change classes Change Trajectory Analysis

  29. Trajectories of Land Cover Change

  30. Conclusions • The multi-temporal change detection analysis indicates a increasing trend in agricultural intensification in the watershed • Western part: expansion of agriculture on Ultisols and karst topography • Eastern part: moderate to weak expansion in agriculture on Spodosols and clayey sand

  31. Module 2 Quantify the spatial distribution of soil nitrate-nitrogen across the SFRW

  32. Develop a site selection protocol to address the spatial variability of nitrate-nitrogen across the watershed using GIS techniques • Soil sampling • Laboratory analysis of nitrate-nitrogen • Compare different interpolation techniques and identify the method with lowest prediction error • Interpret soil nitrate-nitrogen in context of land resources within the SFRW Tasks

  33. Stratified Random Sampling Design Land-use and soil combination raster (Illustrated here are the soil orders present under the urban land use class)

  34. Soil nitrate-nitrogen values (g/g soil) • 101 sites were approved for September 2003 sampling • Soil samples were collected at Layer 1 (0 to 30 cm), Layer 2 (30 to 60 cm), Layer 3 (60 to 120 cm) and Layer 4 (120 to 180 cm)

  35. Layer 1 Spline with tension RMSPE: 1.455 Layer 2 Spline with tension RMSPE: 1.369

  36. Layer 3 Inverse Distance Weighted RMSPE:1.904 Layer 4 Inverse Distance Weighted RMSPE:1.462

  37. Average profile concentrations Spline with tension RMSPE: 1.306

  38. Pixel Based Prediction of Soil Nitrate-Nitrogen Based on LULC-soil combinations • Average nitrate-nitrogen profile values for each LULC-soil combination OPixel soil-N PPixel soil-N

  39. Pixel-Based Prediction of Soil Nitrate-Nitrogen

  40. Conclusion • This analysis is the first step in characterizing the spatio-temporal variation of nitrate-nitrogen at a watershed scale • The LCLU and the soil data support developing predictive models of soil nitrate-nitrogen in the SFRW

  41. Module 3 Water Quality Analysis

  42. Objective Characterize the geographic position and distribution of land resources to understand spatial relationships between watershed characteristics and water quality data Materials Surface water and ground water quality data from SRWMD

  43. Surface Water Quality Observations Time frame of observations: 1989 to 2003

  44. Sub-Basin Attributes • Land use / land cover class (2000) • Soil order (SSURGO) • Geology • Mean, maximum and minimum DRASTIC values • Mean, maximum and minimum soil organic carbon • Mean, maximum and minimum population • Mean, maximum and minimum elevation • Mean, maximum and minimum slope

  45. N-NO3 Results

More Related