The Dongting Lake Estuary is migration pathways for some river-lake migratory and semi-migratory fishes. In the present study, an annual survey of fish was conducted from January to November 2018 covering a total of 6 sites in Dongting Lake Estuary. A total of 57 freshwater species and subspecies belonging to 5 orders and 10 families were recorded. The catches at the Dongting Lake Estuary were mainly composed of Lake settled fish. The biomass of <i>Cyprinus</i> ( <i>Cyprinus </i>) <i>carpio </i> Linnaeus was the highest, accounting for 25.53% of the total catches, followed by <i>Hypophthalmichthys molitrixs </i>, <i>Culter alburnus </i> Basilewsky and <i>Ctenopharyngodon idellus </i>, accounting for 10.41%, 8.99% and 7.10% of the total catches, respectively. The four major domestic carps accounted for 26.13% of the total catch. The range of richness of species varied between 40 and 51 species. The trend was fewer species in spring, with the arrival of summer and autumn gradually increasing, peaking at the turn of summer and autumn, and then gradually decreasing with the arrival of winter, to the lowest in spring. The Shannon, Simpson, Pielou and Margalef indices showed the consistent trends with richness of species.
Dongting Lake is a large, shallow lake in northeastern Hunan Province, China. It is a flood basin of the Yangtze River [
However, as the basin economy develops and human activities aggravate, the Dongting Lake Estuary is confronted with a series of problems of resources and environment such as water environment deterioration, ecological degradation and destruction of resources [
In this study, an annual survey of the composition and diversity of fish communities in the Dongting Lake Estuary was carried out. The objectives are: 1) to characterize the fish fauna in Dongting Lake Estuary; 2) to know fish biodiversity and temporal distribution.
The agricultural watershed, Located in northeastern Hunan Province, China, Dongting Lake (N28˚44' - 29˚35'; E111˚53' - 113˚05') is a large river connected lake in the middle reaches of the Yangtze floodplain. The present study was conducted in the Dongting Lake Estuary, which is a channel of 14 km length and 1 km mean width, and the sampling area was close to Dongting brige, Chenglingji and Sanjiangkou (
Samplings of fish were conducted from January to November 2018, covering a total of 6 sites in Dongting Lake Estuary. Each site was carried out four times. The investigations were conducted by boat. In this way, information was obtained for each cienaga during the four characteristic periods of the hydrological cycle of the Dongting Lake Estuary. The fish were collected using experimental multifilament gillnets, formed from panels measuring 100 × 3 m, in nine different sizes (from 4 to 15 cm stretched mesh).
The nets were set out for 24 h, and checked every 4 h, with the intention of avoiding phenomenon such as predators and decomposition due to the high temperature of the water. In order to estimate the total richness of the species, sampling was designed for each of the various existing habitats. In all the cienagas, one sampling station was chosen within each of these four macrohabitats: littoral with trees, littoral without trees, pelagic, and the connecting channel between cienaga and main rivers. All were sampled simultaneously. Because sampling effort was constant across samples, it was not necessary to adjust diversity estimates using rarefaction or other techniques to account for different sampling techniques or sample sizes.
After sampling a specific site, each individual was identified to the species level according to Chu et al. [
We define the richness of species in a cienaga as Local Richness. Shannon-Wiener diversity ( H ′ ) , Simpson, Pielou and Margalef indices were calculated from the taxonomic composition of cienagas samples [
P i = N i / N × 100 %
Margalef index: R = ( S − 1 ) / ln N ;
Shannon-Wiener diversity ( H ´ ) : H ´ = − ∑ P i ⋅ log 2 P i ;
Simpson index: D = 1 − ( Σ P i ) 2 ;
Pielou evenness index: E = H / H max ;
H max = ln S .
where S is the number of species; N is the number of individuals; Ni is the number of the species i.
During the study, a total of 5831 individuals were recorded representing 57 freshwater species and subspecies in Dongting Lake Estuary, which distributed among 5 orders and 10 families. Cypriniformes and Siluriformes were the most represented orders. The most diverse family was Cyprinidae with thirty-seven species (
As revealed by species accumulation curve (sample-based rarefaction curve,
| Species | Individual % | Weight % | Species | Individual % | Weight % |
|---|---|---|---|---|---|
| Mylopharyngodon piceus (Rich.) | 0.54% | 3.97% | Sarcocheilichthys sinensis sinensis Bleeker | 0.32% | 0.03% |
| Ctenopharyngodon idellus (C.et V.) | 1.58% | 7.10% | S.nigripinnis nigripinnis (Günther) | 0.22% | 0.01% |
| Hypophthalmichthys molitrix (C.et V.) | 3.49% | 10.41% | Coilia brachygnathus Kreyenberg et Pappenheim | 3.78% | 1.17% |
| Aristichthys nobilis (Rich.) | 1.80% | 4.65% | Squalidus argentatus | 1.15% | 0.07% |
| Elopichthys bambusa (Rich.) | 0.61% | 0.51% | Saurogobio dabryi Bleeker | 4.00% | 0.56% |
| Cyprinus (Cyprinus) carpio Linnaeus | 5.80% | 25.53% | Rhinogobio typus Bleeker | 0.68% | 0.25% |
| Carassius auratus auratus (L.) | 5.94% | 3.05% | Saurogobio gymnocheilus Lo, Yao et Chen | 0.36% | 0.02% |
| Parabramis pekinensis (Basilewsky, 1855) | 1.91% | 1.51% | Hemibarbus maculatus Bleeker | 0.97% | 0.58% |
| Pseudobrama simoni (Bleeker) | 0.65% | 0.11% | Sinobdella sinensis | 0.29% | 0.03% |
| Megalobrama skolkovii (Dybowski, 1872) | 0.32% | 0.41% | Mastacembelus armatus (Lac.) | 0.04% | 0.02% |
| Megalobrama amblycephala Yih | 2.23% | 2.32% | Leptobotia taeniops (Savage) | 0.94% | 0.07% |
| Xenocypris argentea Günther | 2.27% | 0.50% | Parabotia fasciata Dabry | 0.07% | 0.01% |
| Xenocypris davidi Bleeker | 0.40% | 0.09% | Abbottina rivularis (Basilewsky) | 1.51% | 0.07% |
| Squaliobarbus curriculus (Rich.) | 3.85% | 3.56% | Channa argus (Cantor) | 1.33% | 1.27% |
| Culter alburnus Basilewsky | 4.32% | 8.99% | Pelteobagrus vachelli (Rich.) | 0.11% | 0.03% |
| Culter mongolicus Basilewsky | 2.63% | 2.21% | Pelteobagrus fulvidraco (Rich.) | 4.47% | 0.90% |
| Culter dabryi | 0.68% | 0.34% | Pelteobagrus nitidus (S.et D.) | 3.49% | 1.48% |
| Cultrichthys erythropterus | 1.62% | 1.29% | Pelteobagrus eupogon (Boulenger) | 0.40% | 0.11% |
| Erythroculter dabryi (Bleeker) | 0.07% | 0.04% | Mystus macropterus (Bleeker) | 0.43% | 0.13% |
| Erythroculter oxycephaloides (Kreyenberg et Pappenheim, 1908) | 0.47% | 0.62% | Pseudorasbora parva (Temminck et Schlegel) | 3.49% | 0.23% |
| Hemiculter leucisculus (Basil.) | 4.07% | 0.56% | Acheilognathus macropterus (Bleeker) | 1.98% | 0.16% |
| Hemiculter bleekeri (Warpachowski, 1887) | 1.62% | 0.13% | Odontobutis obscurus (T.et S.) | 0.14% | 0.01% |
| Rhodeinae | 0.43% | 0.04% | Leiocassis longirostris Günther | 0.11% | 0.50% |
| Siniperca chuatsi (Basil.) | 1.15% | 0.60% | Leiocassis albomar ginatus Rendhal | 0.54% | 0.14% |
| Siniperca kneri Garman | 0.32% | 0.78% | Opsariichthys bidens | 0.04% | 0.01% |
| Siniperca asotus L. | 1.51% | 3.54% | Pseudolaubuca sinensis Bleeker | 0.18% | 0.05% |
| Silurus meridionalis Chen | 0.97% | 1.54% | Onychostoma barbatum (S. Y. Lin, 1931) | 0.07% | 0.02% |
| Coreius heterodon (Bleeker) | 2.27% | 1.43% | others | 15.30% | 6.18% |
| Hyporhamphus intermedius (Cantor) | 0.04% | 0.04% | 100% | 100% |
a high proportion of rare species and few abundant species have a species accumulation curve with a low inflection point on the y-axis and a long upward sloping line to the asymptote.
The catches at the Dongting Lake Estuary were mainly composed of Lake settled fish. The biomass of Cyprinus (Cyprinus) carpio Linnaeus was the highest,
accounting for 25.53% of the total catches, followed by Culter alburnus Basilewsky, Ctenopharyngodon idellus, accounting for 10.41%, 8.99% and 7.10% of the total catches, respectively. Bighead carp (Hypophthalmichthys nobilis), silver carp (H. molitrix), black carp (Mylopharyngodon piceus) and grass carp (Ctenopharyngodon idella) accounted for 26.13% of the total catch (
The abundance, biomass and richness varied seasonally depending on the cienaga, as well as between species. The range of richness of species (local richness) varied between 40 and 51 species, and according to the season of the year (
The Yangtze floodplain is among the largest floodplains in the world. Historically, all lakes in the floodplain were freely connected with the mainstem of the river. At present, only three medium- to large-sized lakes, Dongting Lake, Poyang Lake and Shijiu Lake, retain their free connection with the mainstem of the river. Such river-lake connections maked for the exchange of matter, energy and organisms between the river and its floodplain maintaining fish diversity in this region. The literature shows that Dongting Lake had 104 to 114 species of fish [
Four major domestic carps (blue carp, grass carp, silver carp and Bighead carp) are drifting eggs. In the 1960s, the proportion of fish production in Dongting Lake reached 21%, and then gradually declined (except in 1998 when a large-scale flood occurred). The years before the Three Gorges impoundment were between 8% and 9%. From 2004 to 2009, the rapid decline period was caused by the changes of the hydrological situation and discharge of Dongting Lake after the closure of the Three Gorges. From 2010 to 2017 [
| Indices | Spring | Summer | Autum | Winter |
|---|---|---|---|---|
| No. of species | 42 | 48 | 51 | 40 |
| Shannon | 2.70 | 2.99 | 3.18 | 2.78 |
| Simpson | 0.8677 | 0.9107 | 0.9404 | 0.8519 |
| Pielou | 0.697237 | 0.809813 | 0.850799 | 0.708204 |
| Margalef | 5.867629 | 6.68866 | 6.080415 | 5.94163 |
Species number and diversity indices showed that fish diversity of the Dongting Lake Estuary was high, with temporal variations. Generally, higher diversities occurred in summer and autumn than spring and winter. The periodic changes of fish species number and diversity indices in Dongting Lake estuary coincide with the periodic changes of flood peak and water level in Dongting Lake. Summer and autumn were the peak periods of floods. The Dongting Lake received the flood and got the supplement of fish resources, the species number and fish diversity indices reached the peak at this time. Then, with the recession of floods and the decline of water level, the number of species decreased gradually. The connection between rivers and lakes had play an important role in supplementing the fish resources of Dongting Lake and maintaining the fish diversity of Dongting Lake. The variation trend of diversity indices and evenness indice in Dongting Lake estuary was consistent, indicating that fish in Dongting Lake estuary enjoyed good niche differentiation. Both diversity index and evenness index were suitable for assessing the diversity status of fish in Dongting Lake.
An annual survey of fish was conducted in January to November 2018 in Dongting Lake Estuary. A total of 57 freshwater species and subspecies belonging to 5 orders and 10 families were recorded. The catches at the Dongting Lake Estuary were mainly composed of Lake settled fish. The four major domestic carps accounted for 26.13% of the total catch. The species, Shannon, Simpson, Pielou and Margalef indices, had the consistent trend, which was the fewer species in spring, with the arrival of summer and autumn gradually increasing, peaking at the turn of summer and autumn, and then gradually decreasing with the arrival of winter.
The authors declare no conflicts of interest regarding the publication of this paper.
Yuan, X.P., Yang, X., Ge, H.Z., Li, H. and Deng, D.Q. (2019) Temporal Distribution of Fish Community Structure in Dongting Lake Estuary. Agricultural Sciences, 10, 294-301. https://doi.org/10.4236/as.2019.103025