Title:
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Reedbed mapping using remotely sensed data
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In the UK reedbeds dominated by Phragmites australis have been identified as a
priority habitat for most regional Biodiversity Partnerships. Information on the
current distribution and quality of reedbed sites across the UK is lacking, yet such
information is vital in developing suitable management plans for the conservation
and expansion of this threatened habitat. The focus of this thesis is to develop a
suitable methodology for accurately mapping the distribution and assessing the
biophysical properties of reedbed habitats using remotely sensed data. Three study
sites situated in the North West region of the UK were used: Leighton Moss
nature reserve in Lancashire, and the River Leven and Esthwaite Water situated in
Cumbria. The remotely sensed data used in this study included high-resolution
satellite and airborne imagery and ground-based spectral data.
Results of the first analytical chapter (i.e. chapter 3) demonstrated the potential
of using high resolution QuickBird multi spectral satellite imagery to derive
accurate maps of reedbeds through appropriate analysis of image texture, careful
selection of input bands, spatial degradation of input bands, selection of a suitable
classification algorithm and post-classification refinement using terrain data.
Results of the second analytical chapter (chapter 4) demonstrated the benefits of
using multi-seasonal images over single-date images and the effectiveness of
incorporating spectral bands with textural measures. Through careful selection of
appropriate classification technique, the input image datasets could be used to
generate optimal reedbed maps.
The results of the multi-seasonal reedbed mapping experiment conducted using
QuickBird imagery was the basis for the field spectrometry experiment. The study
aimed at monitoring and understanding variations in the spectral reflectance and
biophysical properties of reedbeds canopies throughout the seasonal phenological
cycle and to identify the optimal spectral indices for quantifying biophysical
properties (chapter five ). The results of the experiment indicated that the narrow-
band derived Difference Vegetation Index (DV I) and Renormalised Difference
Vegetation Index (RDVI) provided the most accurate e'~~iIi1~tes of the leaf area
index (LAl) for reedbed canopies (r = 0.77 and 0.72 respectively).
Having observed the limitations of accurately deriving canopy heights from
experiments conducted in chapter 5, the potential for quantifying canopy
biophysical properties from light detection and radar (LiDAR) data (elevation and
intensity) was investigated in chapter 6. The study demonstrated some of the
potential and limitations of using LiDAR data for characterising reedbed
canopies. A canopy height model (CHM) was generated by subtracting the
Ordnance Survey (OS) derived digital terrain model (DTM) from the LiDAR-
derived digital surface model (DSM). The density of first return points was high
for reedbeds and these were able to generate an accurate CHM, when validated
against field measurements. LiDAR intensity data displayed specular reflection
along the centre of the flight line over reedbeds and water bodies, but not for other
land cover/vegetation types. The LiDAR intensity data showed potential for
containing considerable information on reedbed canopy structure and pattern that
is valuable from an ecological perspective.
Results of the final analytical chapter (chapter 7) demonstrated the value in
combining appropriately compressed hyperspectral imagery with LiDAR data for
the effective mapping of reedbed habitats. The most effective image compression
technique was the spectrally segmented principal component analysis (SSPCA),
which had the optimal combination of reedbed accuracy and processing
efficiency. A substantial improvement in the accuracy of reedbed delineation was
achieved when a mask generated by applying a 3m threshold to the LiDAR-
derived CHM was used to filter the reedbed map derived from the optimal SSPCA
image dataset. Based on the fmdings of chapter 5 and 6, the hyperspectral and LiDAR data was used to derive LAI and canopy height (CH) maps of reedbeds
respectively, two vital biophysical measures needed in estimating the quality of
reedbed canopies. Hence, this study is a step forward in utilizing spectral, spatial
and structural data contained in remotely sensed data for the mapping of reedbed
quantity and quality.
This research has demonstrated the potential of using remotely sensed data,
complemented with adequate ground based information for mapping the spatial
extent and quality of reedbed canopies in three specific sites across the North
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West region in the UK. Based on the success with a specific habitat type,
suggestions are made to further expand these techniques to explore fine scale
mapping of more habitats using remotely sensed data of high spatial resolution.
Hence, two major studies are recommended for future work, namely (1) updating
the Phase 1 habitat survey map using remote sensing techniques, and (2) the
integration of high spatial resolution satellite imagery (hyperspectral or
QuickBird) and LiDAR data for vegetation mapping and deriving biophysical
measures.
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