550 likes | 702 Views
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
E N D
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 km2 • Encompasses parts of Suwannee, Gilchrist, Columbia, Union, Bradford, Alachua, Baker and Clay • Administratively, Suwannee River Water Management District (SRWMD)
DRASTIC Index Depth to water Net recharge Aquifer media Soil media Topography Impact of the vadose zone Hydraulic conductivity
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.
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
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
Module 1 Land cover dynamics in the SFRW
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
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
Landsat TM • August 26th 1990 • August 13th 2000 • Landsat ETM+ • February 11th 2003 Path 17, Row 39
Methods • Design of a land cover classification scheme • Ground truth data collection • Image processing • Change trajectory analysis
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
Ground Truth Data Collection • 487 Ground Control Points (GCP’s) • Categorization into training and accuracy assessment sites (60% / 40%)
Preprocessing Image Processing • Geometric correction • Atmospheric correction • Noise removal • Pre-classification scene stratification • Image classification (Supervised approach) • Accuracy assessment
Correction for distortions in platform attributes Preprocessing:Geometric Correction 2000 Landsat image imposed over the 2003 image RMS error: 0.5 pixel
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)
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.
Preprocessing: Noise Removal Masking cloud and cloud shadow Cloud / cloud shadow infested image Cloud / cloud shadow mask Cloud / cloud shadow masked image of SFRW
Pre-Classification Scene Stratification To separate spectrally similar classes of urban, agriculture and rangeland
Image Classification: Training Stage • Numerical descriptors of land cover classes • Two sets of spectral signatures were developed Winter scene Summer scene
Minimum Distance to Mean Classifier (MDM) Image Classification: Classification Stage
2000 1990 Image Classification: Output Stage
2003 Image Classification: Output Stage Overall classification accuracy: 82%
Three data change image of land cover change classes Change Trajectory Analysis
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
Module 2 Quantify the spatial distribution of soil nitrate-nitrogen across the SFRW
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
Stratified Random Sampling Design Land-use and soil combination raster (Illustrated here are the soil orders present under the urban land use class)
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)
Layer 1 Spline with tension RMSPE: 1.455 Layer 2 Spline with tension RMSPE: 1.369
Layer 3 Inverse Distance Weighted RMSPE:1.904 Layer 4 Inverse Distance Weighted RMSPE:1.462
Average profile concentrations Spline with tension RMSPE: 1.306
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
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
Module 3 Water Quality Analysis
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
Surface Water Quality Observations Time frame of observations: 1989 to 2003
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
N-NO3 Results