Kuo-Wei Lan

Dr. Kuo-Wei Lan

orcid

Research Focus & Metrics

Academic Career Length

11Years (2016-Present)

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

Representative Publications

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5 May 2017 in Remote Sensing
Verified
Journal Article
Open access
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KLKuo-Wei Lan
Kuo-Wei Lan
TSTeruhisa Shimada
Teruhisa Shimada
Ming-An LeeMing-An Lee
Ming-An Lee
NSNan-Jay Su
Nan-Jay Su
Yi ChangYi Chang
Yi Chang
Changes in marine environments affect fishery resources at different spatial and temporal scales in marine ecosystems. Predictions from species distribution models are available to parameterize the environmental characteristics that influence the biology, range, and habitats of the species of interest. This study used generalized additive models (GAMs) fitted to two spatiotemporal fishery data sources, namely 1° spatial grid and observer record longline fishery data from 2006 to 2010, to investigate the relationship between catch rates of yellowfin tuna and oceanographic conditions by using multispectral satellite images and to develop a habitat preference model. The results revealed that the cumulative deviances obtained using the selected GAMs were 33.6% and 16.5% in the 1° spatial grid and observer record data, respectively. The environmental factors in the study were significant in the selected GAMs, and sea surface temperature explained the highest deviance. The results suggest that areas with a higher sea surface temperature, a sea surface height anomaly of approximately −10.0 to 20 cm, and a chlorophyll-a concentration of approximately 0.05–0.25 mg/m3 yield higher catch rates of yellowfin tuna. The 1° spatial grid data had higher cumulative deviances, and the predicted relative catch rates also exhibited a high correlation with observed catch rates. However, the maps of observer record data showed the high-quality spatial resolutions of the predicted relative catch rates in the close-view maps. Thus, these results suggest that models of catch rates of the 1° spatial grid data that incorporate relevant environmental variables can be used to infer possible responses in the distribution of highly migratory species, and the observer record data can be used to detect subtle changes in the target fishing grounds.

9 February 2022 in Fisheries Research
Verified
Journal Article
Closed access
MNMuhamad Naimullah
Muhamad Naimullah
WLWei-Yu Lee
Wei-Yu Lee
YWYan-Lun Wu
Yan-Lun Wu
YCYi-Kai Chen
Yi-Kai Chen
YHYu-Cih Huang
Yu-Cih Huang
KLKuo-Wei Lan
Kuo-Wei Lan

1 June 2018 in Fisheries Oceanography
Verified
Journal Article
Closed access
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KLKuo-Wei Lan
Kuo-Wei Lan
MLMing‐An Lee
Ming‐An Lee
CCChin‐Pei Chou
Chin‐Pei Chou
AVAli Haghi Vayghan
Ali Haghi Vayghan

19 February 2021 in Remote Sensing
Verified
Journal Article
Open access
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PHPo-Yuan Hsiao
Po-Yuan Hsiao
TSTeruhisa Shimada
Teruhisa Shimada
KLKuo-Wei Lan
Kuo-Wei Lan
Ming-An LeeMing-An Lee
Ming-An Lee
CLCheng-Hsin Liao
Cheng-Hsin Liao
The Taiwan Bank (TB) is located in the southern Taiwan Strait, where the marine environments are affected by South China Sea Warm Current and Kuroshio Branch Current in summer. The bottom water flows upward along the edge of the continental shelf, forming an upwelling region that is an essential high-productivity fishing ground. Using trophic dynamic theory, fishery resources can be converted into primary production required (PPR) by primary production, which indicates the environmental tolerance of marine ecosystems. This study calculated the PPR of benthic and pelagic species, sea surface temperature (SST), upwelling size, and net primary production (NPP) to analyze fishery resource structure and the spatial distribution of PPR in upwelling, non-upwelling, and thermal front (frontal) areas of the TB in summer. Pelagic species, predominated by those in the Scombridae, Carangidae families and Trachurus japonicus, accounted for 77% of PPR (67% of the total catch). The benthic species were dominated by Mene maculata and members of the Loliginidae family. The upwelling intensity was the strongest in June and weakest in August. Generalized additive models revealed that the benthic species PPR in frontal habitats had the highest deviance explained (28.5%). Moreover, frontal habitats were influenced by NPP, which was also the main factor affecting the PPR of benthic species in all three habitats. Pelagic species were affected by high NPP, as well as low SST and negative values of the multivariate El Niño–Southern Oscillation (ENSO) index in upwelling habitats (16.9%) and non-upwelling habitats (11.5%). The composition of pelagic species varied by habitat; this variation can be ascribed to impacts from the ENSO. No significant differences were noted in benthic species composition. Overall, pelagic species resources are susceptible to climate change, whereas benthic species are mostly insensitive to climatic factors and are more affected by NPP.

1 August 2018 in Marine and Coastal Fisheries
Verified
Journal Article
Open access
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CLCheng-Hsin Liao
Cheng-Hsin Liao
KLKuo-Wei Lan
Kuo-Wei Lan
HHHsin-Ying Ho
Hsin-Ying Ho
KWKae-Yih Wang
Kae-Yih Wang
YWYan-Lun Wu
Yan-Lun Wu
Predictions from species distribution models are used to parameterize the environmental factors that influence the biology, distribution, and habitats of a species of interest. We fitted generalized additive models (GAMs) to spatiotemporal fishery data from torchlight fishing (2009–2013) to investigate the catch rates of swordtip squid Uroteuthis edulis in relation to changes in oceanographic conditions within the southern East China Sea, and we developed a habitat preference model. A high Jensen–Shannon divergence (JSD) value is considered to be an index of a thermal front. The results obtained using the selected GAMs revealed that the explained deviance in the catch rates pertaining to the oceanographic conditions was 45.10% throughout the year. All variables examined—sea surface temperature (SST), chlorophyll‐a, sea surface height anomaly, and JSD—were statistically significant predictors (P < 0.05), and JSD explained the greatest amount of deviance (17.70%). The model predicted relatively high abundance of swordtip squid at 27–28°N in the southern East China Sea during spring and a decrease from June to August. The high abundance occurred again in September and extended southwestwardly to a region including coastal mainland China. These results demonstrated that high swordtip squid abundance occurred in an SST range of 20.0–26.0°C and a JSD range of 0.35–0.50 during spring around 27–28°N, and movement toward the southwest corresponded with shifts in the Kuroshio front (26°C isotherm) in summer and autumn.

12 August 2022 in Scientific Reports
Verified
Journal Article
Open access
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YWYan-Lun Wu
Yan-Lun Wu
KLKuo-Wei Lan
Kuo-Wei Lan
KEKaren Evans
Karen Evans
YCYi-Jay Chang
Yi-Jay Chang
JCJui-Wen Chan
Jui-Wen Chan
Spatial variations in tuna population and abundance are strongly linked to large-scale climate fluctuations, such as the Pacific decadal oscillation (PDO) and Atlantic multidecadal oscillation (AMO). However, the mechanisms underlying the association of climate indices with yellowfin tuna (YFT) abundance and habitat preference remain unclear. We analysed long-term longline fishery data for YFT and oceanic climate variability index data for 1971–2018. The standardized catch per unit effort (CPUE) of Indo-Pacific Ocean YFT was higher during negative AMO and positive PDO phases. In tropical Pacific Ocean, the trend of YFT habitat preference exhibited seesaw patterns because of the distinct environmental factors influenced by the PDO phase. The PDO changed the environmental parameters throughout the tropical Indian Ocean such that the habitat preference of YFT remained consistent throughout. However, the variations in habitat suitability did not correspond to the distribution or standardized CPUE of YFT throughout the Pacific Ocean during AMO events. Moreover, the changes in habitat suitability had a positive periodicity of 8–16 years with AMO in the Indian Ocean, but revealed opposite trends with the distribution or standardized CPUE of YFT. Our results provide sufficient information to distinguish the variations between PDO phase changing and YFT standardized CPUE/ habitat preference. Furthermore, the AMO phase shift period 60–100 years longer than that of the PDO (20–30 years), and models employing time series of fishery and environmental data must be extended the time period of our study to make the AMO match the fishery data more complete.