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The exotic American eel in Taiwan: ecological implications

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BRIEF COMMUNICATION

The exotic American eel in Taiwan: ecological implications

Y.-S. H

*, C.-H. Y*, H.-T. Y*, C.-W. C*, I-C. L† 

W.-N. T

*‡

*Institute of Zoology, College of Science, National Taiwan University, Taipei, Taiwan, R.O.C. and †Taiwan Fisheries Research Institute, 199 Hou-Ih Road, Keelung, Taiwan,

R.O.C.

(Received 28 July 2001, Accepted 22 May 2002)

Six American eels Anguilla rostrata were identified in the Kaoping River of south-western Taiwan by sequencing the mitochondrial cytochrome b gene (mtCyt-b). This was the first record of an exotic eel species in the natural waters of Taiwan. The exotic eels may have been imported from North America at the elver stage for aquaculture and escaped from culture ponds.  2002 The Fisheries Society of the British Isles. Published by Elsevier Science Ltd. All rights reserved.

Key words: Anguilla rostrata; species identification; mitochondrial cytochrome b gene.

Anguillid eels are catadromous fishes that spawn in the ocean and develop in fresh water (Tesch, 1977). There are 15 described species and 3 subspecies of anguillid eels (Ege, 1939;Castle & Williamson, 1974). All anguillids are Indo-Pacific except the European eel

Anguilla anguilla (L.) and the American eel Anguilla rostrata (LeSueur) inhabiting the

North Atlantic Ocean. In Taiwan, there are four native anguillid eels: Anguilla japonica Temminck and Schlegel, Anguilla marmorata Quoy and Gaimard, Anguilla bicolor

pacifica Schmidt, and Anguilla celebesensis Kaup (Han et al., 2001;Tzeng, 1982;Tzeng & Tabeta, 1983). The Japanese eel A. japonica is a commercially important species for aquaculture in Taiwan. As the catch of Japanese eel elvers has been deemed insufficient to meet the demand of eel aquaculture (Tzeng, 1996), elvers of exotic eel species, mainly American eel and European eel, have been imported since 1969 and 1977, respectively (Li, 1997). In Japan, European eels have been found in the Shinjiko Lake and Mikawa

Bay (Zhang et al., 1999), and are abundant in the Uono River (Aoyama et al., 2000). To

date, no exotic eels have been documented in the natural waters of Taiwan. The external morphologies of native and introduced eels are quite similar, complicating the identifi-cation of exotics. In this study, exotic eel species were identified by phylogenetic analysis of the mitochondrial cytochrome b gene (mtCyt-b). In addition, the age, growth and maturity of exotic eels were examined to evaluate the condition of introduced eels in the natural environment of Taiwan.

Among 184 eels collected from the Kaoping River of south-western Taiwan between July 1999 and February 2001, six individuals, four females (AR1 to AR4) and two males

(AR5 and AR6), were found that differed morphologically from Japanese eels. These eels

had thick snouts, round heads, abundant mesenteric fat and unusually large eyes. Their

total length (LT), body mass, and horizontal and vertical diameters of the left eye were

measured and compared with those of Japanese eels. The ocular index was calculated

according to Pankhurst (1982). Maturation stages of eels were divided into silver,

pre-silver and yellow stages by the colouration of the pectoral fins and the dorsal region

‡Author to whom correspondence should be addressed. Tel.: +886 2 23639570; fax: +886 2 23636837; email: wnt@ccms.ntu.edu.tw

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as well as by silver colour on the belly and the state of gonadal development. Vertebral counts were determined from soft X-ray photographs. Sex was determined by gonadal histology. Maturation stages of ovary and testis were classified according toYamamoto & Yamauchi (1974)andMiura et al. (1991), respectively. Sagittal otoliths of these eels

were extracted and prepared for age determination followingTzeng et al. (1994). DNA

was extracted from the liver tissues of the six unknown individuals and eleven randomly selected individuals of A. japonica (AJ, n=10), and A. marmorata (AM, n=1). The two oligonucleotide primers used for PCR amplification of the mitochondrial cytochrome b

gene, named Cyt-b1 (5 -TGCTAACGATGCCCTAGTGG-3 ) and Cyt-b2 (5 -CTAGT

CAACCTACTAATGGG-3 ), were designed based on the conserved regions of

cytochrome b sequences of the genus Anguilla deposited in GenBank/NCBI. The locations of Cyt-b1 and Cyt-b2 are at nucleotides 39–58 and 1098–1117, respectively, in the open reading frame of the mtCyt-b. After PCR, both strands (1079 bp length) were sequenced commercially (Mission Biotech Inc., Taipei, Taiwan). DNA sequences of the six unknown individuals (AR1–AR6) and other known eel species were then aligned with those of 15 anguillid species deposited in the GenBank using Clustal W (v1.81) network service. A phylogenetic tree was constructed by the neighbour-joining method with genetic distance calculated by Kimura’s two-parameter model using the programme

MEGA 2 (Kumar et al., 2001).

The total length and body mass of the six unknown eels were comparable to those of

Japanese eels (Table I). Their ocular indexes ranged between 6·71 and 20·71 (Table I),

however, markedly larger than those of Japanese eels (1·87–6·90, Table I). Such large

eyes are known only in some American eel specimens (Vladykov, 1973). The gonads of

the unknown eels were intermingled with adipocytes [Fig. 1(a), (b)], similar to those of

American eels (Wenner & Musick, 1974), but different from Japanese eels (Fig. 1(c), (d)]. The numbers of vertebrae of these six eels ranged between 105 and 107, overlapping with

the range of American eels (103–109) (Ege, 1939), but markedly less than Japanese eels

(112–119) (Ege, 1939). Mesenteric fat was abundant in the six individuals, in contrast to the low level of mesenteric fat in Japanese eels. Topology of the phylogenetic tree showed that the six unknown eels, AR1 to AR6, formed a clade with the American eel with

robust bootstrap support (Fig. 2). The mtCyt-b sequences of the six eels showed

low nucleotide differences (AR1–AR6, 1,9,6,7,8,5, respectively) compared to that of American eel deposited (AF006716) with mean transition : transvertion ratio of 4·14, and all of these nucleotide differences were synonymous except AR2, which had four nonsynonymous sites. The mtCyt-b sequences of the six eels could be clearly

distinguished from the closest species European eel (48–53 nucleotides difference).

Hence, the six unknown eels were validated to be American eel A. rostrata.

According to the sexual maturation of Japanese eel (Yamamoto & Yamauchi, 1974),

one female of the exotic eels was at the pre-silver stage with oocytes in the peri-nucleolus stage and the lipid vesicles apparent at the periphery of the oocyte. The other three

T I. Comparison of morphological and gonadal characteristics between the unknown eels and Japanese eels

Unknown eels Japanese eels

Sample size 6 178 Sex composition 84 72 8154 724 LT(mm) 415–700 362–785 Body mass (g) 125–591 55–829 Age (year) 8–12 3–11 No. of vertebrae 105–107 112–119* Ocular index (OI) 6·71–20·71 1·87–6·90 Oocyte diameter (m) 90–150 25–225

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females were already in the silver stage with oocytes in the oil-droplet stage with a mean diameter >140 m [Table IandFig. 1(a)].

It seems impossible that American eels had migrated naturally from the North Atlantic

to Asia (Tsukamoto & Aoyama, 1998) and the only possible route would seem to be

human transplantation. The six exotic American eels may have been discarded by a culturist or escaped from culture ponds and have inhabited the natural waters of Taiwan for years (Table I). They were found to be at the silver stage in July and October, which is somewhat earlier than that of Japanese eels (August to February) in the rivers of Taiwan. The overlap in time of metamorphosis from yellow to silver eel between native Japanese eels and exotic American eels may lead to the risk of interspecific hybridization. Since the spawning ground of the American eel is in the Sargasso Sea, North Atlantic (Schmidt, 1925), and the routes of eel migration are believed to be species-specific (Tsukamoto, 1992), the American eel in Taiwan is unlikely to propagate successfully. As the life cycle and larval transport routes (e.g. North Equatorial Current and Kuroshio Current in Japanese eel; North Equatorial Current and Gulf Stream in American eel) of both eel species are very similar to each other (Cheng & Tzeng, 1996;Wang & Tzeng,

1998, 2000), however, the possibility that American eels may establish new spawning

grounds in Asia cannot be excluded. A migrating European eel in the silver phase was

captured in the East China Sea (Aoyama et al., 2000), indicating that the spawning

migration of introduced eels is possible.

The potential ecological impacts of exotic eel species on native eels may be significant: (a) exotic eels may introduce pathogens and parasites to which native eel species were previously unexposed; (b) exotic eels may compete with native eel species for space and food; (c) interspecific hybridization may cause a disturbance of local gene pools. Hence, the policy of stocking non-native eel species to make up the shortage of Japanese eels in

Taiwan should be re-evaluated carefully. Instead, management efforts should focus on

the protection of native eels to sustain pure populations of this species.

F. 1. Microscopic histology of the gonads stained with haematoxylin and eosin (magnification 200). (a) Female American eel, 612 mm LT, 519·2 g. (b) Male American eel, 415 mm LT, 125·1 g. (c) Female Japanese eel, 695 mm LT, 775·4 g. (d) Male Japanese eel, 494 mm LT, 177·7 g. , adipocytes.

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This study was financially supported by the National Science Council, Taiwan (Grant No. NSC-89-2313-B002-077). The authors are grateful to G. H. Cheng for samples collection and age determination and J. T. He for gonad histological section.

References

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AR1 (AF485271) A. rostrata AR3 (AF485273) AR6 (AF485276) AR5 (AF485275) AR2 (AF485272) AR4 (AF485274) 71 71 100 95 89 54 A. anguilla A. australis schmidti A. australis australis A. dieffenbachii 100 45 32 100 A. interioris A. borneensis A. nebulosa nebulosa A. nebulosa labiata 100 86 34 44 A. obscura A. bicolor bicolor A. bicolor pacifica 100 60 85 AM (AF485278) A. marmorata A. celebesensis A. megastoma A. reinhardti 92 63 29 89 0.01 100 AJ (AF485277) A. japonica A. mossambica

F. 2. Phylogenetic tree constructed with the neighbour-joining method. The coding region sequences of mtCyt-b of six exotic American eels (AR1–AR6), one selected A. japonica (AJ), one A. marmorata (AM), and 18 known eel species and subspecies obtained from GenBank/NCBI were used for analysis. The accession numbers of this study were shown as indicated. The numbers represent bootstrap values of 1000 replicates. Accession numbers: A. rostrata, AF006716; A. anguilla, AF006714; A. dieffenbachii, AF006711; A. australis schmidti, AB021769; A. australis australis, AF006712; A. interioris, AB021773; A. borneensis (synonym of A. malgumora), AF006718; A.

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