Hideyuki Niwa

Dr. Hideyuki Niwa

Faculty of Bioenvironmental Sciences, Kyōto, Japan
orcid

Research Focus & Metrics

Academic Career Length

17Years (2010-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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6 September 2019 in Landscape and Ecological Engineering
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Journal Article
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LZLinying Zhang
Linying Zhang
YOYui Oyake
Yui Oyake
YMYukihiro Morimoto
Yukihiro Morimoto
HNHideyuki Niwa
Hideyuki Niwa
SSShozo Shibata
Shozo Shibata

10 February 2020 in Landscape and Ecological Engineering
Verified
Journal Article
Closed access
PDF file
LZLinying Zhang
Linying Zhang
YOYui Oyake
Yui Oyake
YMYukihiro Morimoto
Yukihiro Morimoto
HNHideyuki Niwa
Hideyuki Niwa
SSShozo Shibata
Shozo Shibata


28 June 2011 in Aquatic Conservation: Marine and Freshwater Ecosystems
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Journal Article
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TOTakeshi Osawa
Takeshi Osawa
HMHiromune Mitsuhashi
Hiromune Mitsuhashi
HNHideyuki Niwa
Hideyuki Niwa
AUAtushi Ushimaru
Atushi Ushimaru


14 February 2023 in Remote Sensing
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Journal Article
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HNHideyuki Niwa
Hideyuki Niwa
HIHajime Ise
Hajime Ise
MKMahito Kamada
Mahito Kamada
Investigating the three-dimensional structure of mangrove forests is critical for their conservation and restoration. However, mangrove forests are difficult to survey in the field, and their 3D structure is poorly understood. Light detection and ranging (LiDAR) is considered an accurate and dependable method of measuring the 3D structure of mangrove forests. This study aimed to find a suitable LiDAR platform for obtaining attributes such as breast height diameter and canopy area, as well as for measuring a digital terrain model (DTM), the base data for hydrological analysis. A mangrove forest near the mouth of the Oura River in Aza-Oura, Nago City, Okinawa Prefecture, Japan, was studied. We used data from terrestrial LiDAR scanning “TLS” and unmanned aerial vehicle (UAV) LiDAR scanning “ULS” as well as data merged from TLS and ULS “Merge”. By interpolating point clouds of the ground surface, DTMs of 5 cm × 5 cm were created. DTMs obtained from ULS could not reproduce the heaps of Thalassina anomala or forest floor microtopography compared with those obtained from TLS. Considering that ULS had a few point clouds in the forest, automatic trunk identification could not be used to segment trees. TLS could segment trees by automatically identifying trunks, but the number of trees identified roughly doubled that of the visual identification results. The number of tree crowns identified using TLS and ULS was approximately one quarter of those identified visually, and many of them were larger in area than the visually traced crowns. The accuracy of tree segmentation using the canopy height model (CHM) was low. The number of canopy trees identified using Merge produced the best results, accounting for 61% of the visual identification results. Results of tree segmentation by CHM suggest that combining TLS and ULS measurements may improve tree canopy identification. Although ULS is a promising new technology, its applications are clearly limited, at least in mangrove forests such as the Oura River, where Bruguiera gymnorhiza is dominant. Depending on the application, using different LiDAR platforms, such as airborne LiDAR scanning, UAV LiDAR scanning, and TLS, is important. Merging 3D point clouds acquired by different platforms, as proposed in this study, is an important option in this case.