Research Article |
Corresponding author: E Zhang ( zhange@ihb.ac.cn ) Academic editor: Maria Elina Bichuette
© 2022 Xiao Chen, Man Wang, E Zhang.
This is an open access article distributed under the terms of the Creative Commons Attribution License (CC BY 4.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Citation:
Chen X, Wang M, Zhang E (2022) Updated species checklist of fishes from Lake Dongting in Hunan Province, South China: Species diversity and conservation. ZooKeys 1108: 51-88. https://doi.org/10.3897/zookeys.1108.79960
|
A lack of an updated checklist of freshwater fish species from Lake Dongting is a great hindrance to further biodiversity analysis. A seasonal survey of fishes in the lake was conducted from October 2017 to January 2019. Based on the data obtained during the field survey and coupled with known literature and the latest taxonomic development of relevant taxa, the species checklist of fishes from Lake Dongting was updated. A total of 130 species from 12 orders, 30 families and 76 genera has been documented, containing 126 native species and four alien species. Its fish fauna is dominated by the Xenocyprididae that has the highest number of included species (30), followed by the Gobionidae (25) and Acheilognathidae (11). This checklist comprises 20 species undergoing nomenclatural changes and 11 new records, eight of which are native and three exotic. It excludes 20 species, which have been reported in error in historical works, due to synonyms, erroneous records, taxonomic changes and unconfirmed records. Unsampled in this survey were 34 species that are ecologically specialised: migratory, rheophilic, predatory, shellfish-dependent or pelagic-egg-spawning. While some of these species eluded capture likely due to the paucity of population, others may have been extirpated in Lake Dongting perhaps owing to human perturbations, such as river damming across affluents or the Chang-Jiang mainstem, sand dredging, overfishing or water pollution. The updated checklist lays a sound foundation for biodiversity conservation of fishes in Lake Dongting.
Annotated list, biodiversity, ichthyofauna, taxonomy, threatened species
Freshwater ecosystem and freshwater fish may well face one of the greatest threats in the world in the context of global biodiversity crisis (
The freshwater ecosystem of the Chang-Jiang (= Yangtze River; Jiang, Shui and He in Chinese mean river), the third largest river of the world and the largest river of China, supports rich biodiversity of aquatic organisms (
The aquatic biodiversity of Lake Dongting is greatly imperilled by anthropogenic activities, like sand dredging, overfishing, alien species invasion, water pollution from industrial, agricultural and domestic sewage discharges and so forth (
An updated checklist of fishes from Lake Dongting remains to be provided. The first checklist of freshwater fishes from this lake was given by
The taxonomic history of fishes from Lake Dongting could be traced back to the mid-19th century. Père Heude, a French Jesuit catholic priest, made a collection of fish specimens at the lake from 1869 to 1884 (
More studies were focused on the species inventory of fishes from Lake Dongting following the establishment of P. R. China in 1949. Forty-three species of the lake were involved in
As from the 1990s, increasing research interests have centred on the fish diversity of Lake Dongting. Survey of fishery resources carried out by
Lake Dongting (28°44'N–29°35'N, 111°53'E–113°05'E) is located in the northern part of Hunan Province, connected to the middle Chang-Jiang mainstem (
Twenty sampling sites were selected in this study, based on habitat heterogeneity (Fig.
All collected specimens were identified to species level. The initial identification in the field principally followed
In addition to the data collected during our field sampling, known research works were referred. Reference was made to the following main historical records of fishes in the lake:
Fish classifications are being transformed greatly as latest molecular phylogenies provide evidence in support for natural groups which were unanticipated by previous studies (
A total of 130 fish species, identified from 12 orders, 30 families and 76 genera, have been documented from Lake Dongting (Table
Annotated checklist of the fish fauna from Lake Dongting. The species under each family or subfamily are sorted by alphabetical order. Notes are labelled with taxonomic alteration, synonymisation, misidentification and other meanings.
Valid species name | Previous studies | Note |
---|---|---|
Acipenseriformes | ||
Acipenseridae | ||
001 Acipenser dabryanus Duméril, 1869 | ○P | |
002 Acipenser sinensis Gray, 1835 | ○D | |
Polyodontidae | ||
003 Psephurus gladius (Martens, 1862) | ○D | |
Anguilliformes | ||
Anguillidae | ||
004 Anguilla japonica Temminck & Schlegel, 1846 | ⊕D | |
Clupeiformes | ||
Clupeidae | ||
005 Tenualosa reevesii (Richardson, 1846) | ○D | |
Engraulidae | ||
006 Coilia brachygnathus Kreyenberg & Pappenheim, 1908 | ⊕P | |
007 Coilia nasus Temminck & Schlegel, 1846 | ○D | |
Cypriniformes | ||
Catostomidae | ||
008 Myxocyprinus asiaticus (Bleeker, 1864) | ⊕P | |
Botiidae | ||
009 Leptobotia citrauratea (Nichols, 1925) | ⊕P | |
Leptobotia elongata (Bleeker, 1870) | ⊙M | |
010 Leptobotia rubrilabris (Dabry de Thiersant, 1872) | ○P | |
011 Leptobotia taeniops (Sauvage, 1878) | ⊕P | |
012 Parabotia banarescui (Nalbant, 1965) | ⊕P | |
013 Parabotia fasciata Dabry de Thiersant, 1872 | ⊕P | |
Cobitidae | ||
014 Cobitis macrostigma Dabry de Thiersant, 1872 | ⊕P | |
015 Cobitis sinensis Sauvage & Dabry de Thiersant, 1874 | ⊕P | |
016 Misgurnus anguillicaudatus (Cantor, 1842) | ⊕P | |
017 Paramisgurnus dabryanus Dabry de Thiersant, 1872 | ⊕P | |
Balitoridae | ||
018 Lepturichthys fimbriatus (Günther, 1888) | ○P | |
Cyprinidae | ||
Labeoninae | ||
019 Cirrhinus cirrhosus Bloch, 1795 | +AP | |
020 Cirrhinus molitorella (Valenciennes, 1844) | ⊕AP | |
021 Decorus tungting (Nichols, 1925) | Bangana tungting (Nichols, 1925) | ○TP |
022 Pseudogyrinocheilus prochilus (Sauvage & Dabry de Thiersant, 1874) | +P | |
Cyprininae | ||
023 Carassius auratus (Linnaeus, 1758) | ⊕P | |
Cyprinus carpio Linnaeus, 1758 | ⊙T | |
024 Cyprinus rubrofuscus Lacepède, 1803 | ⊕P | |
Procypris rabaudi (Tchang, 1930) | ⊙M | |
Acrossocheilinae | ||
025 Onychostoma rarum (Lin, 1933) | ○P | |
026 Onychostoma simum (Sauvage & Dabry de Thiersant, 1874) | ○P | |
Spinibarbinae | ||
027 Spinibarbus caldwelli (Nichols, 1925) | ○P | |
Spinibarbus hollandi Oshima, 1919 | ⊙T | |
Spinibarbus sinensis Bleeker, 1871 | ⊙M | |
Xenocyprididae | ||
028 Aristichthys nobilis (Richardson, 1845) | ⊕P | |
029 Chanodichthys dabryi (Bleeker, 1871) | Culter dabryi Bleeker, 1871 | ⊕TP |
030 Chanodichthys erythropterus (Basilewsky, 1855) | Culter alburnus Basilewsky, 1855 | ⊕TP |
031 Chanodichthys mongolicus (Basilewsky, 1855) | Culter mongolicus Basilewsky, 1855 | ⊕TP |
032 Chanodichthys oxycephalus (Bleeker, 1871) | Culter oxycephalus Bleeker, 1871 | ○TP |
033 Chanodichthys oxycephaloides (Kreyenberg & Pappenheim, 1908) | Culter oxycephaloides Kreyenberg & Pappenheim, 1908 | ⊕TP |
034 Culter alburnus (Basilewsky, 1855) | Cultrichthys erythropterus (Basilewsky, 1855) | ⊕TP |
035 Ctenopharyngodon idella (Valenciennes, 1844) | ⊕P | |
036 Distoechodon tumirostris Peters, 1881 | ○P | |
037 Elopichthys bambusa (Richardson, 1845) | ⊕P | |
038 Hemiculter bleekeri Warpachowski, 1888 | ⊕P | |
039 Hemiculter leucisculus (Basilewsky, 1855) | ⊕P | |
040 Hypophthalmichthys molitrix (Valenciennes, 1844) | ⊕P | |
041 Luciobrama macrocephalus (Lacepède, 1803) | ○P | |
042 Megalobrama amblycephala Yih, 1955 | ⊕P | |
043 Megalobrama mantschuricus (Basilewsky, 1855) | Megalobrama skolkovii Dybowski, 1872 | ⊕SP |
044 Mylopharyngodon piceus (Richardson, 1846) | ⊕P | |
045 Ochetobius elongatus (Kner, 1867) | ○P | |
046 Opsariichthys bidens Günther, 1873 | ⊕P | |
047 Parabramis pekinensis (Basilewsky, 1855) | ⊕P | |
048 Plagiognathops microlepis (Bleeker, 1871) | Xenocypris microlepis Bleeker, 1871 | ○TP |
049 Pseudobrama simoni (Bleeker, 1864) | ⊕P | |
050 Pseudolaubuca engraulis (Nichols, 1925) | ○P | |
051 Pseudolaubuca sinensis Bleeker, 1864 | ⊕P | |
052 Sinibrama macrops (Günther, 1868) | ⊕P | |
Sinibrama wui (Rendahl, 1933) | ⊙S | |
053 Squaliobarbus curriculus (Richardson, 1846) | ⊕P | |
054 Toxabramis swinhonis Günther, 1873 | ⊕P | |
055 Xenocypris davidi Bleeker, 1871 | ⊕P | |
056 Xenocypris macrolepis Bleeker, 1871 | Xenocypris argentea Günther, 1868 | ⊕SP |
057 Zacco acanthogenys (Boulenger, 1901) | ⊕P | |
Zacco platypus (Temminck & Schlegel, 1846) | ⊙T | |
Acheilognathidae | ||
058 Acheilognathus barbatulus Günther, 1873 | +P | |
059 Acheilognathus barbatus Nichols, 1926 | ○P | |
060 Acheilognathus chankaensis (Dybowski, 1872) | ○P | |
061 Acheilognathus gracilis Nichols, 1926 | ⊕P | |
Acheilognathus imberbis Günther, 1868 | ⊙U | |
062 Acheilognathus hypselonotus (Bleeker, 1871) | ○P | |
063 Acheilognathus macromandibularis Doi, Arai & Liu, 1999 | +P | |
064 Acheilognathus macropterus (Bleeker, 1871) | ⊕P | |
065 Acheilognathus polylepis (Wu, 1964) | ⊕P | |
066 Acheilognathus tonkinensis (Vaillant, 1892) | ○P | |
Acheilognathus taenianalis (Günther, 1873) | ⊙S | |
067 Rhodeus ocellatus (Kner, 1866) | ⊕P | |
068 Rhodeus sinensis Günther, 1868 | ⊕P | |
Gobionidae | ||
069 Abbottina rivularis (Basilewsky, 1855) | ⊕P | |
070 Coreius heterodon (Bleeker, 1864) | ⊕P | |
Coreius guichenoti (Sauvage & Dabry de Thiersant, 1874) | ⊙M | |
071 Gobiobotia filifer (Garman, 1912) | ⊕P | |
072 Gobiobotia meridionalis Chen & Cao, 1977 | Gobiobotia longibarba meridionalis Chen & Cao, 1977 | ⊕TP |
073 Gobiobotia nicholsi Bănărescu & Nalbant, 1966 | ○P | |
074 Gobiobotia lii Chen, Wang, Cao & Zhang, 2022 | +P | |
Gobiobotia pappenheimi Kreyenberg, 1911 | ⊙M | |
Xenophysogobio boulengeri (Tchang, 1929) | ⊙M | |
075 Hemibarbus labeo (Pallas, 1776) | ⊕P | |
076 Hemibarbus maculatus Bleeker, 1871 | ⊕P | |
077 Microphysogobio tungtingensis (Nichols, 1926) | ⊕P | |
078 Paracanthobrama guichenoti Bleeker, 1864 | ⊕P | |
079 Pseudogobio vaillanti (Sauvage, 1878) | +P | |
080 Pseudorasbora parva (Temminck & Schlegel, 1846) | ⊕P | |
081 Rhinogobio cylindricus Günther, 1888 | ○P | |
082 Rhinogobio typus Bleeker, 1871 | ⊕P | |
083 Rhinogobio ventralis Sauvage & Dabry de Thiersant, 1874 | ○P | |
Sarcocheilichthys kiangsiensis Nichols, 1930 | ⊙T | |
084 Sarcocheilichthys nigripinnis (Günther, 1873) | ⊕P | |
085 Sarcocheilichthys tungtingensis Nichols & Pope, 1927 | ○P | |
086 Sarcocheilichthys sinensis Bleeker, 1871 | ⊕P | |
087 Saurogobio dabryi Bleeker, 1871 | ⊕P | |
088 Saurogobio dumerili Bleeker, 1871 | ○P | |
089 Saurogobio gymnocheilus Lo, Yao & Chen, 1998 | ⊕P | |
090 Saurogobio gracilicaudatus Yao & Yang, 1977 | +P | |
091 Saurogobio lissilabris Bănărescu & Nalbant, 1973 | ⊕P | |
092 Saurogobio xiangjiangensis Tang, 1980 | +P | |
093 Squalidus argentatus (Sauvage & Dabry de Thiersant, 1874) | ⊕P | |
Squalidus nitens (Günther, 1873) | ⊙U | |
Siluriformes | ||
Bagridae | ||
094 Hemibagrus macropterus Bleeker, 1870 | Mystus macropterus (Bleeker, 1870) | ⊕P |
095 Tachysurus crassilabris (Günther, 1864) | Leiocassis crassilabris Günther, 1864 | ⊕TP |
096 Tachysurus dumerili (Bleeker, 1864) | Leiocassis longirostris Günther, 1864 | ⊕TP |
097 Tachysurus eupogon (Boulenger, 1892) | Pelteobagrus eupogon (Boulenger, 1892) | ⊕TP |
098 Tachysurus mica (Gromov, 1970) | Leiocassis argentivittatus (Regan,1905) | +TP |
099 Tachysurus nitidus (Sauvage & Dabry de Thiersant, 1874) | Pelteobagrus nitidus (Sauvage & Dabry de Thiersant, 1874) | ⊕TP |
100 Tachysurus sinensis (Lacepède, 1803) | Pelteobagrus fulvidraco (Richardson, 1846) | ⊕TP |
Tachysurus tenuis (Günther, 1873) | ⊙M | |
101 Tachysurus ussuriensis (Dybowski, 1872) | Pseudobagrus ussuriensis (Dybowski, 1872) | ○TP |
102 Tachysurus vachellii (Richardson, 1846) | Pelteobagrus vachellii (Richardson, 1846) | ⊕TP |
103 Tachysurus zhangfei Shao, Cheng & Zhang, 2021 | Pseudobagrus albomarginatus (Rendahl, 1928) | ⊕TP |
Amblycipitidae | ||
104 Liobagrus aequilabris Wright & Ng, 2008 | ⊕P | |
Sisoridae | ||
105 Glyptothorax sinensis (Regan, 1908) | ⊕P | |
Siluridae | ||
106 Silurus asotus Linnaeus, 1758 | ⊕P | |
107 Silurus meridionalis Chen, 1977 | ⊕P | |
Ictaluridae | ||
108 Ictalurus punctatus (Rafinesque, 1818) | +AP | |
Osmeriformes | ||
Salangidae | ||
109 Hemisalanx prognathus Regan, 1908 | ⊕F | |
Hemisalanx brachyrostralis (Fang, 1934) | ⊙S | |
110 Neosalanx brevirostris (Pellegrin, 1923) | ○F | |
Neosalanx taihuensis Chen, 1956 | ⊙S | |
111 Neosalanx jordani Wakiya & Takahashi, 1937 | ○F | |
Neosalanx oligodontis Chen, 1956 | ⊙S | |
112 Protosalanx hyalocranius (Abbott, 1901) | ○F | |
Gobiiformes | ||
Odontobutidae | ||
113 Micropercops cinctus (Dabry de Thiersant, 1872) | Micropercops swinhonis (Günther, 1873) | ⊕SV |
114 Odontobutis sinensis Wu, Chen & Chong, 2002 | ⊕V | |
Gobiidae | ||
115 Mugilogobius myxodermus (Herre, 1935) | ○V | |
Rhinogobius brunneus (Temminck & Schlegel, 1845) | ⊙U | |
116 Rhinogobius cliffordpopei (Nichols, 1925) | ○V | |
117 Rhinogobius similis Gill, 1859 | ⊕V | |
Rhinogobius giurinus Gill, 1859 | ⊙S | |
Synbranchiformes | ||
Mastacembelidae | ||
118 Sinobdella sinensis (Bleeker, 1870) | ⊕P | |
Synbranchidae | ||
119 Monopterus albus (Zuiew, 1793) | ⊕P | |
Anabantiformes | ||
Osphronemidae | ||
120 Macropodus opercularis (Linnaeus, 1758) | ⊕P | |
Channidae | ||
121 Channa argus (Cantor, 1842) | ⊕P | |
122 Channa asiatica (Linnaeus, 1758) | ⊕P | |
Beloniformes | ||
Hemiramphidae | ||
123 Hyporhamphus intermedius (Cantor, 1842) | ⊕V | |
Adrianichthyidae | ||
124 Oryzias latipes (Temminck & Schlegel, 1846) | ○F | |
Tetraodontiformes | ||
Tetraodontidae | ||
125 Takifugu obscurus (Abe, 1949) | ○D | |
Centrarchiformes | ||
Centrarchidae | ||
126 Micropterus salmoides (Lacepède, 1802) | +AP | |
Sinipercidae | ||
127 Siniperca chuatsi (Basilewsky, 1855) | ⊕P | |
128 Siniperca knerii Garman, 1912 | ⊕P | |
129 Siniperca roulei Wu, 1930 | Coreosiniperca roulei (Wu, 1930) | ⊕TP |
130 Siniperca scherzeri Steindachner, 1892 | ⊕P |
For species richness, the order representing the greatest number of species were Cypriniformes (86 species, 66.15% of the total), followed by the Siluriformes (15, 11.54%), Centrarchiformes (5, 3.85%), Gobiiformes (5, 3.85%), Osmeriformes (4, 3.08%), Anabantiformes (3, 2.31%), Clupeiformes (3, 2.31%), Acipenseriformes (3, 2.31%), Synbranchiformes (2, 1.54%), Beloniformes (2, 1.54%), Tetrodontiformes (1, 0.77%) and Anguilliformes (1, 0.77%). The family Xenocyprididae has the highest number (30) of fish species, accounting for 23.08% of the total, followed by the Gobionidae and Acheilognathidae, with 25 and 11 species contributing to 19.23% and 8.46%, respectively. The subsequent families included the Bagridae (10, 7.69%), Cyprinidae (9, 6.92%) and so forth (Table
Order | Family | Genus | Species |
---|---|---|---|
Acipenseriformes | Acipenseridae | 1 | 2 |
Polyodontidae | 1 | 1 | |
Anguilliformes | Anguillidae | 1 | 1 |
Clupeiformes | Clupeidae | 1 | 1 |
Engraulidae | 1 | 2 | |
Cypriniformes | Catostomidae | 1 | 1 |
Botiidae | 2 | 5 | |
Cobitidae | 3 | 4 | |
Balitoridae | 1 | 1 | |
Cyprinidae | 7 | 9 | |
Xenocyprididae | 22 | 30 | |
Acheilognathidae | 2 | 11 | |
Gobionidae | 12 | 25 | |
Siluriformes | Bagridae | 2 | 10 |
Amblycipitidae | 1 | 1 | |
Sisoridae | 1 | 1 | |
Siluridae | 1 | 2 | |
Ictaluridae | 1 | 1 | |
Osmeriformes | Salangidae | 3 | 4 |
Gobiiformes | Odontobutidae | 2 | 2 |
Gobiidae | 1 | 3 | |
Synbranchiformes | Mastacembelidae | 1 | 1 |
Sybranchidae | 1 | 1 | |
Anabantiformes | Osphronemidae | 1 | 1 |
Channidae | 1 | 2 | |
Beloniformes | Hemiramphidae | 1 | 1 |
Adrianichthyidae | 1 | 1 | |
Tetraodontiformes | Tetraodontidae | 1 | 1 |
Centrarchiformes | Centrarchidae | 1 | 1 |
Sinipercidae | 1 | 4 | |
12 | 30 | 76 | 130 |
Lake Dongting harboured 27 migratory fishes, six of which are diadromous and 21 potamodromous, and 103 sedentary fishes, accounting for 20.77% and 79.23% of the total freshwater fishes, respectively. There are 113 (86.92% of the total species) primary freshwater fishes (species spending the whole life in freshwater;
The updated checklist of fishes from Lake Dongting includes 49 species endemic to China, 22 endemic to the Chang-Jiang and nine endemic to the mid-lower Chang-Jiang, respectively. This survey yielded 35 Chinese endemics (accounting for 71.43% of the total Chinese endemics from Lake Dongting), 13 endemic species of the Chang-Jiang (59.09% of the total endemic species of the river from the lake) and six endemic species of the mid-lower Chang-Jiang (66.67% of the total endemic species of these reaches from the lake), respectively.
The updated checklist of fishes in Lake Dongting recognises a total of 130 species, based on the data collected in this survey and historical records. Amongst them, 93 native fish species were observed in this fish survey, including eight new records (See Table
The Acipenseridae has two representatives in the lake, namely Acipenser sinensis Gray, 1835 and A. dabryanus Duméril, 1869, while the Polyodontidae is presented only by a single species Psephurus gladius. All three large-sized sturgeons were not collected in Lake Dongting during this field survey. One juvenile individual (4340 mm SL, 566.0 g) of A. sinensis was collected from East Dongting Lake during the 2012–2013 field survey (unpublished data). The specimen is likely a captive-bred individual released into the wild. This conservation measure has been implemented in the upper Chang-Jiang Basin for nearly twenty years (
Anguilla japonica Temminck & Schlegel, 1846, a delicious food fish of economic importance in China and even across the Globe, is the only representative of the family in Lake Dongting. Historically, the lake and its affluents were utilised by this catadromous fish as feeding grounds (
The family Clupeidae and Tetraodontidae are each represented in Lake Dongting by a single species. The two diadromous fishes, Tenualosa reevesii and Takifugu obscurus (Abe, 1949), are hardly seen in this lake so far. The last capture of T. reevesii (one individual) was at Jiangsu provincial section of the Chang-Jiang in 1998 (
This family has only two representatives in Lake Dongting: Coilia brachygnathus and C. nasus Temminck & Schlegel, 1846. So far, C. brachygnathus abounds in this lake where it is a delicious food fish of economic importance, but C. nasus is a rarely encountered fish. Coilia nasus is even regarded to have been extinct due to anthropogenic interferences for nearly two decades (
This family has four representatives in Lake Dongting: Hemisalanx prognathus, Neosalanx brevirostris (Pellegrin, 1923), N. jordani Wakiya & Takahashi, 1937 and Protosalanx hyalocranius (Abbott, 1901). So far, the taxonomy of Chinese icefishes still remains controversial (
This family has a single representative in China: Myxocyprinus asiaticus (Bleeker, 1864). Myxocyprinus asiaticus had long been considered as a migratory fish (
The Cyprinidae, as traditionally delimited, contains species with one to three rows of pharyngeal teeth, barbels present or absent and Weberian apparatus (
This subfamily was newly erected to include species currently designated to Folifer, Onychostoma and Acrossocheilus (
Previously, Cyprinus carpio Linnaeus, 1758 was extensively utilised as the available specific name for the common carp widespread in China. This species, however, is currently regarded as the endemic species of Europe (
This subfamily has four representatives in Lake Dongting: Decorus tungting, Cirrhinus cirrhosus Bloch, 1795, C. molitorella (Valenciennes, 1844) and Pseudogyrinocheilus prochilus (Sauvage & Dabry de Thiersant, 1874). The first species were firstly designated to Sinilabeo Rendahl, 1933 (
The subfamily is represented in Lake Dongting by a single species: Spinibarbus caldwelli (Nichols, 1925). Spinibarbus caldwelli was previously recognised as S. hollandi Oshima, 1919 (
The family is the dominant group of the ichthyofauna of Lake Dongting, with 30 species identified from 22 genera: Aristichthys Oshima, 1919 (one species), Chanodichthys Bleeker, 1860 (five), Ctenopharyngodon Steindachner, 1866 (one), Culter Basilewsky, 1855 (one), Distoechodon Peters, 1881 (one), Elopichthys Bleeker, 1860 (one), Hemiculter Bleeker, 1860 (two), Hypophthalmichthys Bleeker, 1860 (one), Luciobrama Bleeker, 1870 (one), Megalobrama Dybowski, 1872 (two), Mylopharyngodon Peters, 1881 (one), Ochetobius Günther, 1868 (one), Opsariichthys Bleeker, 1863 (one), Parabramis Bleeker, 1864 (one), Plagiognathops Berg, 1907 (one), Pseudobrama Bleeker, 1870 (one), Pseudolaubuca Bleeker, 1864 (two), Sinibrama Wu, 1939 (one),Squaliobarbus Günther, 1868 (one), Toxabramis Günther, 1873 (one), Xenocypris Günther, 1868 (two) and Zacco Jordan & Evermann, 1902 (one). The large majority of these species are widespread in the lowlands of south or east China.
Several previously-recorded species from Lake Dongting have synonymisations or taxonomic changes. Xenocypris argentea Günther, 1868 was synonymised with X. macrolepis Bleeker, 1871 (
The taxonomy of three genera Chanodichthys Bleeker, 1860, Culter Basilewsky, 1855 and Cultrichthys Smith, 1938 is hitherto in a chaotic status in Chinese literature. The type species of Chanodichthys is Leptocephalus mongolicus Basilewsky, 1855 [type locality: China: Mongolia (presently Inner Mongolia Province) and Manchuria (now northeast China)], that of Culter is C. alburnus Basilewsky, 1855 [type locality: China: rivers flowing into the Gulf of Tschili (today’s Hebei Province)] and that of Cultrichthys is C. brevicauda Günther, 1868 (type locality: Taiwan, China).
Twenty-five species of gudgeons from Lake Dongting are placed in 12 genera, namely Abbottina Jordan & Fowler, 1903 (one species), Coreius Jordan & Starks, 1905 (one), Gobiobotia Kreyenberg, 1911 (four), Hemibarbus Bleeker, 1860 (two), Microphysogobio Mori, 1934 (one), Paracanthobrama Bleeker, 1864 (one), Pseudogobio Bleeker, 1860 (one), Pseudorasbora Bleeker, 1860 (one), Rhinogobio Bleeker, 1870 (three), Sarcocheilichthys Bleeker, 1860 (three), Saurogobio Bleeker, 1870 (six) and Squalidus Dybowski, 1872 (one). Most of these species are often seen in the mid-lower Chang-Jiang basin or even lowland areas of the southern China.
Sarcocheilichthys is represented in Lake Dongting by three species, namely S. nigripinnis (Günther, 1873), S. tungtingensis Nichols & Pope, 1927 and S. sinensis Bleeker, 1871. Our ongoing taxonomy of this genus demonstrates that S. kiangsiensis Nichols, 1930 occurs only in the lake Poyang system and that specimens, formerly identified as this species from Lake Dongting, belong to S. tungtingtensis (
Four species of Gobiobotia were formerly reported from Lake Dongting: G. filifer (Garman, 1912), G. meridionalis Chen & Cao, 1977, G. nicholsi Bănărescu & Nalbant, 1966 and G. pappenheimi Kreyenberg, 1911. The first species is to date endemic to the Chang-Jiang Basin downstream of Yibin City. The second species had long been treated as a subspecies of G. longibarba Fang & Wang, 1931 until
The bitterlings have eleven representatives in Lake Dongting: A. macropterus (Bleeker, 1871), A. barbatulus Günther, 1873, A. macromandibularis Doi, Arai & Liu, 1999, A. polylepis (Wu, 1964), A. gracilis, A. barbatus Nichols, 1926, A. chankaensis (Dybowski, 1872), A. tonkinensis (Vaillant, 1892), A. hypselonotus (Bleeker, 1871), Rhodeus ocellatus (Kner, 1866) and R. sinensis Günther, 1868. The first one was formerly misidentified as A. taenianalis (Günther, 1873) (
This family is so far represented in Lake Dongting by five species, three of which are from Leptobotia [L. citrauratea (Nichols, 1925), L. rubrilabris (Dabry de Thiersant, 1872) and L. taeniops (Sauvage, 1878)] and two from Parabotia [P. fasciata Dabry de Thiersant, 1872 and P. banarescui (Nalbant, 1965)].
The taxonomy of the bagrid catfishes from China is notoriously poorly understood. This family is represented in Lake Dongting by two genera: Hemibagrus Bleeker, 1862 and Tachysurus Lacepède, 1803. Species previously referred to Mystus Scopoli, 1777 are misidentification of Hemibagrus in Chinese literature (
The Bagridae is represented in Lake Dongting by 10 species, namely Tachysurus crassilabris (Günther, 1864), T. dumerili (Bleeker, 1864), T. eupogon (Boulenger, 1892), T. mica (Gromov, 1970), T. nitidus (Sauvage & Dabry de Thiersant, 1874), T. sinensis Lacepède, 1803, T. ussuriensis (Dybowski, 1872), T. vachellii (Richardson, 1846), T. zhangfei Shao, Cheng & Zhang, 2021 and Hemibagrus macropterus Bleeker, 1870. Tachysurus dumerili is a senior subjective synonym of T. longirostris Günther, 1864 (
The family Ictaluridae and Centrarchidae are each represented in Lake Dongting by a single species. Ictalurus punctatus (Rafinesque, 1818) and Micropterus salmoides (Lacepède, 1802), introduced as cultured fishes to China, are sporadically found in the lakes from southern China (
This family is so far represented in Lake Dongting by four species of the genus Siniperca Gill, 1862: S. chuatsi (Basilewsky, 1855), S. knerii Garman, 1912, S. roulei Wu, 1930 and S. scherzeri Steindachner, 1892 (
Five gobies of Mugilogobius Smitt, 1900 and Rhinogobius Gill, 1859 were previously recorded from Lake Dongting: M. myxodermus (Herre, 1935), R. brunneus (Temminck & Schlegel, 1845), R. cliffordpopei, R. giurinus Gill, 1859 and R. similis Gill, 1859 (
Lake Dongting, as the second-largest river-connected freshwater lake lying within the floodplain areas of the mid-lower Chang-Jiang Basin, supports diversified freshwater fish species. A total of 130 fish species is here reported from the Lake. This number accounts for ca. 31.48% of the total freshwater fishes of the Chang-Jiang Basin where 413 native species were recently documented (
The total number of freshwater fish species of Lake Dongting given in this updated checklist is actually comparable to that of Lake Poyang, the first-largest river-connected floodplain lake of the mid-lower Chang-Jiang Basin, where a total of 136 fish species has been recorded so far (
The present study shows that fish species diversity of Lake Dongting remains insufficiently understood. The number of species, collected from the Lake in this survey, is lower compared with the frontrunners (
This checklist includes 20 species which experienced nomenclatural alterations, viz. Bangana tungting (= Decorus tungting), Coreosiniperca roulei (= Siniperca roulei), Culter alburnus (= Chanodichthys erythropterus), Culter dabryi (= Chanodichthys dabryi), Culter mongolicus (= Chanodichthys mongolicus), Culter oxycephaloides (= Chanodichthys oxycephaloides), Culter oxycephalus (= Chanodichthys oxycephalus), Cultrichthys erythropterus (= Culter alburnus), Gobiobotia longibarba meridionalis (= Gobiobotia meridionalis), Leiocassis argentivittatus (= Tachysurus mica), Leiocassis crassilabris (= Tachysurus crassilabris), Leiocassis longirostris (= Tachysurus dumerili), Mystus macropterus (= Hemibagrus macropterus) Pelteobagrus eupogon (= Tachysurus eupogon), Pelteobagrus fulvidraco (= Tachysurus sinensis), Pelteobagrus nitidus (= Tachysurus nitidus), Pelteobagrus vachellii (= Tachysurus vachellii), Pseudobagrus albomarginatus (= Tachysurus zhangfei), Pseudobagrus ussuriensis (= Tachysurus ussuriensis), Xenocypris microlepis (= Plagiognathops microlepis). Two species, Gobiobotia nicholsi and Sarcocheilichthys tungtingensis are, for the time being, regarded as valid. Their taxonomic status needs to be confirmed when specimens from their type locality (today’s East Dongting Lake) become available.
Amongst 130 freshwater fish species of Lake Dongting, 12 (9.23% of the total) are labelled as threatened species in
Endemics of the mid-lower Chang-Jiang Basin and protected fish species in Lake Dongting.
Species | CITES | China | Hunan | IUCN | Endemics |
---|---|---|---|---|---|
Psephurus gladius | √ | I | CR | ||
Acipenser sinensis | √ | I | CR | ||
Acipenser dabryanus | √ | I | CR | ||
Coilia nasus | √ | LC | |||
Coilia brachygnathus | DD | √ | |||
Tenualosa reevesii | I | √ | CR | ||
Neosalanx brevirostris | √ | DD | |||
Anguilla japonica | EN | ||||
Myxocyprinus asiaticus | II | √ | CR | ||
Onychostoma simum | √ | NT | |||
Onychostoma rarum | √ | VU | |||
Spinibarbus caldwelli | √ | LC | |||
Luciobrama macrocephalus | II | √ | CR | ||
Ochetobius elongatus | √ | CR | |||
Decorus tungting | √ | EN | √ | ||
Megalobrama amblycephala | LC | √ | |||
Acheilognathus macropterus | LC | √ | |||
Acheilognathus hypselonotus | LC | √ | |||
Acheilognathus macromandibularis | LC | √ | |||
Microphysogobio tungtingensis | √ | DD | √ | ||
Saurogobio gracilicaudatus | LC | √ | |||
Saurogobio xiangjiangensis | √ | LC | |||
Rhinogobio ventralis | II | EN | |||
Leptobotia citrauratea | DD | √ | |||
Leptobotia rubrilabris | II | VU | |||
Siniperca roulei | √ | NT | |||
Channa asiatica | √ | LC | |||
Macropodus opercularis | √ | NT | |||
Total | 3 | 8 | 15 | 9 |
Five species are also on the latest List of Key Protected Wild Animals in China, namely Leptobotia rubrilabris, Luciobrama macrocephalus, Myxocyprinus asiaticus, Rhinogobio ventralis and Tenualosa reevesii (
Besides three species (Luciobrama macrocephalus, Myxocyprinus asiaticus and Tenualosa reevesii), there are another 12 species currently included in Hunan provincial key protected wildlife list (
Lake Dongting harbours nine fish species endemic to the mid-lower Chang-Jiang Basin, namely Acheilognathus hypselonotus, A. macromandibularis, A. macropterus, Coilia brachygnathus, Decorus tungting, Leptobotia citrauratea, Megalobrama amblycephala, Microphysogobio tungtingensis and Saurogobio gracilicaudatus. These species have a high risk of being imperilled by anthropogenic perturbation. More efforts should be dedicated to monitor their population size and trend. Decorus tungting, a popular food fish of local economic importance in Lake Dongting system before 1980s, is currently restricted only to some sections of the Yuan-Jiang and Zi-Shui, two affluents of Lake Dongting (
Thirty-four historically documented fish species were not collected from Lake Dongting during this field survey; their fate is of particular concern. These species fall within five categories. The first one is migrating species, like Acipenser dabryanus, A. sinensis, Coilia nasus, Psephurus gladius, Tenualosa reevesii and Takifugu obscurus. The main reasons for the extirpation of the first four species in the lake are mentioned above. Although the last two species eluded capture during this field survey, both were reportedly collected in exceptional years (
The Chang-Jiang basin is an area with over 400 million residents, highly impacted by anthropogenic interferences. It is also the most rapidly growing area of China’s economic development. The loss of aquatic diversity and, thus, its ecological service function in this river is becoming a pressing challenge. It is urgently needed to take practical actions to conserve the freshwater ecosystem of the Chang-Jiang Basin. To this end, the Chinese government made a decision of implementing the conservation measure of ‘ten-year fishing ban’ in all natural water bodies of the mainstem and major tributaries of the Chang-Jiang since 2020 (
This work was granted by the special fund for Biodiversity Survey & Assessment Project for Biodiversity Conservation of Lake Dongting (2017HB2096001006) and National Science & Technology Fundamental Resources Investigation Program of China (2019FY101800). We are very grateful to Dr. Liang Cao, Chang-Ting An, Li-Jun Zhang, Zi-Tong Wang, Wei-Han Shao, Dong-Ming Guo (IHB), Dinh Tao Nguyen (CCNU), Unisa Conteh Kanu and Long-Hui Qiu (HZAU) for their help with field sampling. Our sincere thanks should go to Prof. Jianzhong Shen (HZAU) for his assistance in fieldworks. Special thanks should be given to Radford Arrindell (AMNH) for providing specimens photographs of Gobiobotia nicholsi, G. pappenheimi, G. filifer and Xenophysogobio boulengeri. We greatly appreciate all valuable comments of two Reviewers Jie Zhang and Fan Li.
Table S1
Data type: Table (docx. file)
Explanation note: Table S1. Geographical coordinates of 20 sampling sites in Lake Dongting.