Abstract

Quantification of reed coverage and vegetation status is fundamental for monitoring and developing lake conservation strategies. The applicability of Unmanned Aerial Vehicles (UAV) three-dimensional data (point clouds) for status evaluation was investigated. This study focused on mapping extent, density, and vegetation status of aquatic reed beds. Point clouds were calculated with Structure from Motion (SfM) algorithms in aerial imagery recorded with Rotary Wing (RW) and Fixed Wing (FW) UAV. Extent was quantified by measuring the surface between frontline and shoreline. Density classification was based on point geometry (height and height variance) in point clouds. Spectral information per point was used for calculating a vegetation index and was used as indicator for vegetation vitality. Status was achieved by combining data on density, vitality, and frontline shape outputs. Field observations in areas of interest (AOI) and optical imagery were used for reference and validation purposes. A root mean square error (RMSE) of 1.58 m to 3.62 m for cross sections from field measurements and classification was achieved for extent map. The overall accuracy (OA) acquired for density classification was 88.6% (Kappa = 0.8). The OA for status classification of 83.3% (Kappa = 0.7) was reached by comparison with field measurements complemented by secondary Red, Green, Blue (RGB) data visual assessments. The research shows that complex transitional zones (water–vegetation–land) can be assessed and support the suitability of the applied method providing new strategies for monitoring aquatic reed bed using low-cost UAV imagery.

Highlights

  • Reed beds located in freshwater lakes around shores can be categorized into three ecological zones

  • This study focused on mapping extent, density, and vegetation status of aquatic reed beds

  • Point clouds were calculated with Structure from Motion (SfM) algorithms in aerial imagery recorded with Rotary Wing (RW) and Fixed Wing (FW) Unmanned Aerial Vehicles (UAV)

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Summary

Introduction

Reed beds located in freshwater lakes around shores can be categorized into three ecological zones. Transitional, and aquatic reeds have been mapped according to the lake’s water level. Land reed grows in rarely flooded areas, has a lower stem density and height compared to the transitional reed, and is a stand mixed with other species (e.g., Thypa, Scripus, Carex). Transitional reed is flooded periodically and has the highest stem density and height. Aquatic reed stands in water throughout the year and forms the reed expansion front, representing the boundary to the lakeside. It is the most sensitive area in a reed stock and, under favorable conditions, it is able to develop further rhizomes and spread lakeward. Aquatic reed is characterized by a lower stem density and a lower height. As well as transitional reed, are normally pure stands consisting of Phragmites australis [1]

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