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Research Article
Species diversity of freshwater glass eel (Anguilliformes, Anguillidae) of Yilan, Taiwan, with remark on two new records
expand article infoYen-Ting Lin, Yu-San Han
‡ National Taiwan University, Taipei, Taiwan
Open Access

Abstract

Yilan, Taiwan is the first place in East Asia where freshwater glass eels, the juvenile stage of Anguilla species, arrive by ocean currents. We collected glass eels by fyke net in Lanyang River estuary twice a month from July 2010 to November 2023. By morphological examination and sequencing of the mitochondrial cytochrome b gene, we identified seven species of Anguilla. Most of the glass eels captured in Yilan belonged to the species A. japonica, A. marmorata, and A. bicolor pacifica. Only a few were A. luzonensis, and two A. celebesensis were recorded. In addition, two species were recorded for the time time from Taiwan; A. interioris and A. borneensis were confirmed by cytochrome b sequencing. Thus, we increase the number of Anguilla species in Taiwan from five to seven.

Key words

Anguilla borneensis, Anguilla interioris, glass eel, new records

Introduction

The freshwater eel (Anguilla spp.) comprises 16 species and three subspecies (Arai 2016a). All Anguilla species are catadromous fish, meaning they migrate to the ocean to spawn (Arai and Chino 2012). The leaf-like larvae of Anguilla species, known as leptocephali, are carried by ocean currents and undergo metamorphosis into eel-like juveniles, which are known as glass eels (Tsukamoto et al. 2002; Hatakeyama et al. 2022). Glass-eel fishing is crucial for the eel aquaculture industry, as there are no artificial reproduction techniques for commercial purposes (Okamura et al. 2014). In Taiwan, the dispersal of glass eels is primarily influenced by the Kuroshio Current (Hsiung et al. 2022b). Yilan, Taiwan, is renowned as the largest glass-eel fishing ground in Taiwan due to its proximity to the Kuroshio. Notably, Yilan holds the distinction of being the first location in East Asia where glass eels arrive, establishing it as a significant hub for this crucial stage in the eel life cycle (Han et al. 2016a).

To date, five Anguilla species have been identified and recorded in Taiwan (Leander et al. 2012; Han et al. 2016b). Among these, A. japonica, A. marmorata, and A. bicolor pacifica are the most prevalent species (Han 2001; Hsu et al. 2019), while A. luzonensis and A. celebesensis are notably very rare and primarily observed as glass eel in Taiwan (Teng et al. 2009; Han et al. 2016b). Previous studies suggest that A. japonica, A. marmorata, and A. bicolor pacifica share a common spawning area near the southern West Mariana Ridge (Kuroki et al. 2009; Arai 2016b), whereas other tropical eel species (A. celebesensis, A. borneensis, A. luzonensis, and A. interioris) have been identified near southern Mindanao Island as their spawning grounds (Aoyama et al. 2003; Wouthuyzen et al. 2009; Arai 2014, 2016b). Due to the morphological challenges in distinguishing tropical eel glass eels (Minegishi et al. 2005), DNA barcoding techniques, as highlighted by Wibowo et al. (2021), provide a precise method for the identification of species. Previous research also indicates that mitochondrial cytochrome b gene fragments are suitable for the identification of freshwater eels (Han et al. 2008). This study aims to analyse glass-eel samples captured in Yilan from July 2010 to November 2023. Through DNA sequencing, the goal is to confirm the number of freshwater glass-eel species transported to Taiwan during this period.

Materials and methods

Sample collection

Glass eels were collected twice a month at night using a fyke net positioned in the estuary of the Yilan River (24.7162°N, 121.8352°E) from July 2010 to November 2023. Following the capture, all the samples were immersed in a 95% ethanol solution for measurement and preservation. All freshwater glass-eel specimens were deposited in the Institute of Fisheries, National Taiwan University (NTUIFS). Recent research adhered to ethical regulations set forth by the Institutional Animal Care and Use Committee (IACUC) under approval number NTU-110-EL-00152.

Morphological measurement

The method for morphological identification of anguillid glass eels was adapted from Han et al. (2012), and the description of the pigmentation stage followed Fukuda et al. (2013). Four morphological parameters were measured using digital callipers with an accuracy of 0.1 mm: total length (TL), head length (HL), pre-dorsal length (PDL), and pre-anal length (PAL). The fin-difference ratio was then calculated using the formula shown below. Glass eels with fin differences exceeding 13% in Yilan were consistently identified as A. marmorata (Han et al. 2012). Therefore, specimens displaying black pigment on the tail and fin differences <13% were chosen for mitochondrial cytochrome b gene sequencing.

 Fin Difference Ratio (%)=PAL( mm)-PDL( mm)TL( mm)×100

Mitochondrial cytochrome b gene sequencing

Freshwater glass-eel specimens with a fin-difference ratio <13% were DNA sequenced for precise identification; these amounted to 281 samples. Genomic DNA was extracted from the dorsal-fin tissue of the glass eels using the FavorPrep Tissue Genomic DNA Extraction Mini Kit (Favorgen, Taiwan). Polymerase chain reaction (PCR) was carried out to amplify a segment of mitochondrial cytochrome b using forward primer: cytb-F (5′-GAT GCC CTA GTG GAT CTA CC-3′) and reverse primer: cytb-R (5′-TAT GGG TGT TCT ACT GGT AT-3′), which was adapted from Han et al. (2008). The resulting PCR product (approximately 1000 bp) was sequenced using the primers cytb-F or cytb-R (by Genomic Biotech Inc., Taiwan), following protocols from Han et al. (2008). Sequencing results were submitted to the National Center for Biotechnology Information (NCBI) GenBank (https://blast.ncbi.nlm.nih.gov/Blast.cgi) to confirm species.

Results

Diversity of freshwater glass eel

A total of 29,442 freshwater glass eels were collected between July 2010 and November 2023. The composition of freshwater glass-eel species is shown in Table 1. Anguilla japonica and A. marmorata were the most prevalent species, comprising 95.4% of our captures (Table 1). Although A. bicolor pacifica and A. luzonensis were infrequently captured, they still represented 3.9% and 0.7% of all specimens, respectively, and two A. celebesensis were also recorded (Table 1). Additionally, two species were found in Taiwan for the first time: A. interioris and A. borneensis (Table 1).

Table 1.

Number of species (n) and percentage contributions of freshwater glass eels collected in Yilan.

Species n Percentage contributions
A. japonica 14217 48.3
A. marmorata 13864 47.1
A. bicolor pacifica 1152 3.9
A. luzonensis 205 0.7
A. celebesensis 2 <0.01
A. interioris 1 <0.01
A. borneensis 1 <0.01

New Anguilla records from Taiwan

The sequencing results of the two new records, total two specimens (NTUIFS IL13’0812-76 and NTUIFS IL21’0715-207), and the best matched BLAST results are shown in Table 2.

Table 2.

Sequencing BLAST results of three new records freshwater glass eel.

Specimen Species Percent identity (%) NCBI accession
NTUIFS IL13’0812-76 Anguilla interioris 99.4 HG965574.1
NTUIFS IL21’0715-207 Anguilla borneensis 99.4 NC_006536.1*

Family Anguillidae

Anguilla interioris Whitley, 1938

Figs 1, 2, Table 3

Material examined

NTUIFS IL13’0812-76, 46 mm TL, off the estuary of the Yilan River, Yilan, northeastern Taiwan (24.7162°N, 121.8352°E), 12 August 2013, fyke net, collected by Yu-San Han.

Figure 1. 

Anguilla interioris (NTUIFS IL13’0812-76), 46 mm TL. Preserved in 95% alcohol. Scale bar: 10 mm.

Short description

PDL 29.3% in TL; PAL 39.1% in TL; fin-difference ratio 9.78%. Body elongate, head length 13.1% TL. The specimen was in fresh condition, with black pigment distributed on the caudal fin and slightly on the caudal peduncle; pigmentation stages VB2 (Fig. 2).

Figure 2. 

Pigmentation on the tail tip of Anguilla interioris (NTUIFS IL13’0812-76).

Distribution

New Guinea (Aoyama et al. 2000); Philippines (glass eel only, Wibowo et al. 2021); Indonesia (leptocephalus only, Kuroki et al. 2006; all stages, Zan et al. 2022); Taiwan (glass eel only, present study).

Table 3.

The morphological parameters of seven freshwater glass eel collected in Yilan.

Species TL (mm) PDL (mm) PAL (mm) Fin-difference ratio (%)
A. japonica 61.1±2.5 15.1±0.9 20.1±0.7 9.2±1.3
A. marmorata 51.4±2.7 11.8±0.8 19.4±1.1 15.5±0.8
A. bicolor pacifica 49.2±2.3 18.3±1.6 18.5±1.6 0.5±0.5
A. luzonensis 52.9±2.7 13.7±0.7 19.4±1.0 11.4±1.1
A. celebesensis 45.3 12.8 17.5 10.4
A. interioris 46.0 13.5 18.0 10.1
A. borneensis 49.5 13.0 18.0 9.8

Remarks

The distribution of A. interioris has been primarily known from only New Guinea (Aoyama et al. 2000). However, a study by Kuroki et al. (2006) documented the leptocephalus of A. interioris in the Indonesian Archipelago, marking the first expansion of the species beyond its then-known range. Additionally, records of A. interioris have been identified using DNA sequencing from Indonesia and southern Mindanao, Philippines (Wibowo et al. 2021; Zan et al. 2022). Herein, we present the first record of A. interioris glass eel from Taiwan.

Anguilla borneensis Popta, 1924

Figs 3, 4, Table 3

Material examined

NTUIFS IL21’0715-207, 49.5 mm TL, off the estuary of the Yilan River, Yilan, northeastern Taiwan (24.7162°N, 121.8352°E), 15 July 2021, fyke net, collected by Yen-Ting Lin.

Figure 3. 

Anguilla borneensis (NTUIFS IL21’0715-207), 49.5mm TL. Preserved in 95% alcohol. Scale bar: 10 mm.

Short description

PDL 26.3% in TL; PAL 36.4% in TL; fin-difference ratio 10.1%. Body extremely elongate, head length 10.1% TL. The specimen was in fresh condition, with black pigment distributed on the caudal peduncle and caudal fin; pigmentation stages VA (Fig. 4).

Figure 4. 

Pigmentation on the tail tip of Anguilla borneensis (NTUIFS IL21’0715-207).

Distribution

Indonesia (Watanabe et al. 2014); Taiwan (glass eel only, present study).

Remarks

The best-matched GenBank accession number for NTUIFS IL21’0715-207 was found to be NC_006536.1, which corresponds to A. malgumora submitted by Minegishi et al. (2005). However, it is noteworthy that A. malgumora was identified as a junior synonym of A. borneensis by Minegishi et al. (2005). Based on the comprehensive examination by Minegishi et al. (2005) and the detailed description provided in NC_006536.1, we can confidently affirm that our specimen NTUIFS IL21’0715-207 is A. borneensis. Herein, we report the first record of A. borneensis outside of the Indonesia (Watanabe et al. 2014).

Discussion and conclusion

Leptocephali and glass eels primarily rely on ocean currents for transport (Kuroki et al. 2016). In Taiwan, the main current responsible for transporting glass eels is the North Equatorial Current (NEC), followed by the Kuroshio, which is known to carry the most abundant anguillid species (A. japonica and A. marmorata) to the region (Hsiung et al. 2022a). Additionally, other tropical eels (A. bicolor pacifica, A. luzonensis, and A. celebesensis) may reach Taiwan via the bifurcation region of the NEC near the Philippine coast, which could potentially transport glass eels from southern Mindanao Island to the Kuroshio (Aoyama et al. 2015; Rudnick et al. 2015). The two species identified in our study align with previous research on the diversity of tropical glass eels (A. celebesensis, A. interioris, and A. borneensis) in southern Mindanao (Shirotori et al. 2016).

Previous research based on differences in Sr:Ca ratios in the leptocephalus otoliths has shown the presence of two populations of A. interioris, with one population in the Indian Ocean and another in the Pacific Ocean (Kuroki et al. 2006). Furthermore, leptocephali of the Pacific Ocean population of A. interioris potentially are transported to Taiwan via the Mindanao Current which ultimately forms a connection with the Kuroshio and the Mindanao Eddy (Kuroki et al. 2006).

The distribution of leptocephali and glass eels of the Indonesian A. borneensis, which is considered the most basal Anguilla species, remains unclear (Aoyama et al. 2001). The spawning area of A. borneensis may overlap with other basal tropical eels (A. celebesensis, A. interioris, A. marmorata, and A. bicolor bicolor) in Indonesia in the western Pacific Ocean (Arai and Abdul Kadir 2017); this suggests the possibility that a similar pathway to Taiwan is followed, as by A. interioris and A. celebesensis (Han et al. 2016b).

Alternatively, it is possible that if A. borneensis and A. interioris establish a new population in the western Pacific Ocean, their larvae could be carried to Taiwan via the North Equatorial Current (NEC) and the Kuroshio. Additionally, some alien freshwater eel species have escaped from aquaculture ponds and have been reported to have similar migration behaviour of native eel in East Asia (Okamura et al. 2002). Examples include A. rostrata, which has been discovered in Taiwanese waters (Han et al. 2002), and the European eel, A. anguilla, which was captured in the East China Sea and Japanese waters (Aoyama 2000; Okamura et al. 2002). Therefore, the possibility of alien eel species establishing new populations in the West Pacific Ocean cannot be discounted, whether caused by human activities (A. rostrata and A. anguilla) or by natural phenomenon (A. interioris and A. borneensis) (Aoyama 2000; Han et al. 2002).

Although there are seven species of freshwater glass eel recorded in Taiwan, only elvers of A. japonica, A. marmorata, A. luzonensis, and A. bicolor pacifica had been found in streams (Tzeng and Tabeta 1983; Watanabe et al. 2013; Hsu et al. 2019). The existence of the elvers and adults of A. celebesensis, A. interioris, and A. borneensis still need confirmation in the field.

In conclusion, the present study increases the number of freshwater glass-eel species in Taiwan from five to seven (Leander et al. 2012; Han et al. 2016b), with the addition two new species records in this paper.

Acknowledgements

We thank Zhen-Hui Chen (local fisherman) for assisting us in setting the fyke net and providing various sampling support; Chien-Hsiang Lin and Hsin-Wei Liu (Biodiversity Research Center, Academia Sinica) for photographing specimens and offering curatorial insights for this research.

Additional information

Conflict of interest

The authors have declared that no competing interests exist.

Ethical statement

No ethical statement was reported.

Funding

The authors extend our gratitude to the National Science and Technology Council, Executive Yuan, Taiwan (MOST 111-2313-B-002-016-MY3) for funding this project.

Author contributions

The experiment and sample collecting were performed by Yu-San Han and Yen-Ting Lin. Yen-Ting Lin write the manuscript. Yu-San Han designed and supervised the experiments. All authors participated in manuscript writing and interpretation of results. All authors read and approved the final manuscript.

Data availability

All of the data that support the findings of this study are available in the main text or Supplementary Information.

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Supplementary materials

Supplementary material 1 

NTUIFS IL13'0812-76 sequencing data

Yen-Ting Lin, Yu-San Han

Data type: txt

Explanation note: The sequencing results of NTUIFS IL13'0812-76.

This dataset is made available under the Open Database License (http://opendatacommons.org/licenses/odbl/1.0/). The Open Database License (ODbL) is a license agreement intended to allow users to freely share, modify, and use this Dataset while maintaining this same freedom for others, provided that the original source and author(s) are credited.
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Supplementary material 2 

NTUIFS IL21'0715-207 sequencing data

Yen-Ting Lin, Yu-San Han

Data type: txt

Explanation note: The sequencing results of NTUIFS IL21'0715-207.

This dataset is made available under the Open Database License (http://opendatacommons.org/licenses/odbl/1.0/). The Open Database License (ODbL) is a license agreement intended to allow users to freely share, modify, and use this Dataset while maintaining this same freedom for others, provided that the original source and author(s) are credited.
Download file (995.00 bytes)
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