Abstract

Woody plant encroachment into grasslands and rangelands is a world-wide phenomenon but detailed descriptions of changes in geographical distribution and infilling rates have not been well documented at large land scales. Remote sensing with either aerial or satellite images may provide a rapid means for accomplishing this task. Our objective was to compare the accuracy and utility of two types of images with contrasting spatial resolutions (1-m aerial and 30-m satellite) for classifying woody and herbaceous canopy cover and determining woody infilling rates in a large area of rangeland (800 km2) in north Texas that has been invaded by honey mesquite (Prosopis glandulosa). Accuracy assessment revealed that the overall accuracies for the classification of four land cover types (mesquite, grass, bare ground and other) were 94 and 87% with kappa coefficients of 0.89 and 0.77 for the 1-m and 30-m images, respectively. Over the entire area, the 30-m image over-estimated mesquite canopy cover by 9 percentage units (10 vs. 19%) and underestimated grass canopy cover by the same amount when compared to the 1-m image. The 30-m resolution image typically overestimated mesquite canopy cover within 225 4-ha sub-cells that contained a range of mesquite covers (1–70%) when compared to the 1-m image classification and was not suitable for quantifying infilling rates of this native invasive species. Documenting woody and non-woody canopy cover on large land areas is important for developing integrated, regional-scale management strategies for rangeland and grassland regions that have been invaded by woody plants.

Highlights

  • Woody plant encroachment on non-agricultural lands is a world-wide phenomenon [1,2,3,4]

  • Mesquite cover was 9 percentage units greater in the 30-m image classification compared to the 1-m image

  • Grassland areas were 9 percentage units and 12% lower in the 30-m image compared to the 1-m image

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Summary

Introduction

Woody plant encroachment on non-agricultural lands (e.g., grasslands and rangelands) is a world-wide phenomenon [1,2,3,4]. Woodland thickets may have utility for ecosystem carbon storage and bioenergy uses [16,17,18]. Because these potentially detrimental and beneficial effects often become significant only at large spatial scales (e.g., impacting livestock grazing, watershed function, wildlife habitat) and at certain density and canopy cover levels [10,11], accurate and detailed mapping of woody distribution at such scales is essential for determining extant conditions and invasion rates and developing long-term management plans for these regions

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