Citation Detail:
HE Shunping and CHEN Yiyu.1996. The Status of the Endangered Freshwater Fishes
The Status of the Endangered Freshwater Fishes of Their Endangerment. in: Conserving
China's Biodiversity (CCICED ed.). China Environmental Science Press.
Wuhan. 169-174p.
The
Status of the Endangered Freshwater Fishes
in
China and Analysis of theCauses
of
Their Endangerment
HE
Shunping and CHEN Yiyu
(Institute of Hydrobiology,
CAS,Wuhan, Hubei 430072)
¥ [Abstract]¥ [Introduction]¥ [The status of endangered freshwater fishes in China]
¥ [Causes of endangerment of the freshwater fishes in China]
Abstract
More than 800species of freshwater
fishes are precious biological resources in the inland water system of China.
Among them, there are a great number of endemic and otherwise precious forms,
and many monotypic genera and species. Recently, owing to a combination of natural
and human-caused events, many of these fishes have gradually become endangered.
Preliminary results indicate that 92 species of fish in China are endangered,
and these account for 10% of the total freshwater fishes in China. For the purpose
of protection of the biodiversity of fishes, it is necessary to analyse the
causes which have led the fishes to become endangered. This report could be
used as a scientific reference for researching and saving the endemic precious
freshwater fishes in China.
Key words: Endangered freshwater fishes, Causes of Endangerment, China
In the process of the evolution of living things, along with the origin of life, the extinction of life also existed. In the long history of life, speciation and extinction of living things often kept a relative balance. Over time, especially as a result of the impact of the activities of human beings, this natural pattern of biodiversity has been altered. Finally, in modern society, the activities of humans have not only accelerated the progress of society and the development of human-based economies, but also have become a major source of disturbance to other species. Human influences upon nature happened all around the globe and are the main factor of the extinction of living things (Solbrig, 1992).
The
same as other living things, the life of freshwater fishes is influenced by
human activity. Economic growth and production has resulted in significant changes
to the environment, so that some regional fishes of economic importance have
become endangered within several decades of unsustainable use. And the structure
of most fish populations has become small sized and lower-aged. At the present
time, not only has the total number freshwater fishes declined, but the number
of species of fish has also decreased.
I. The status of endangered freshwater fishes in China
As a result of the many different geographical environments in China, there
is a very great biodiversity of freshwater fishes (about 900 species). This
biodiversity is a precious biological resource in the inland water system of
China. This biodiversity is comprised of 70% cyprinid fishes, as well as significant
numbers of endemic and precious groups. Many of the forms are of monotypic genera
and monotypic species. These fishes are special and precious research material
to enhance our understanding of phylogenetics and biogeography. And they represent
a very important biological resource for humans. But over the past several decades,
many of these forms have become endangered or extinct. Preliminary results indicate
that 92 species of Chinese freshwater fishes are endangered, and these account
for 10% of the total freshwater fishes in China (Fig. 1). Among them, 52 species
are cyprinid fishes, 11 are catfishes fishes, 5 are sturgeons, 6 are salmon
and 18 species belong to other taxonomic groups of fishes (Tab.1 and Fig. 2).
The degree of imminent danger to these threatened forms may be divided into
4 grades: extinct, rare, endangered and gradual endangered. In Chinese freshwater
fishes, 4 species are extinct, 23 species are rare, 28 species are endangered
and 37 species are gradual endangered (Fig.3).
Table 1. The statistics of endangered freshwater fishes in China
|
Group |
Endangered species |
Total species |
|
Cyprinid |
52 |
600 |
|
Catfish |
11 |
|
|
Sturgeon |
5 |
|
|
Salmons |
6 |
|
|
Others |
18 |
|
|
Total |
92 |
860 |

Figure 1. The percentage of endangered freshwater fishes in China

Figure 2. The statistics of the endangered Chinese freshwater fishes

Figure 3. The statistics of the endangered grade of Chinese freshwater fish
Table 2. The list of the endangered freshwater fishes in China
| EEL: 1-2 | 46. Semilabeo obseurus Lin |
| 1. Lampetra reissneri (Dybowsky) | 47. Ptychidio macrops Fang |
|
2. Lampetra japonica (Martens) |
48. Sinocrossocheilus guizhouensis Wu |
| STURGEON: 3-7 | 49. Placocheilus cryptonemus Cui et Li |
| 3. Acipenser schrencki (Brandt) | 50. Pseudorasbora elongata Wu |
| 4. Acipenser dabryanus Dumeril | 51. Squalidus minor (Harada) |
| 5. Acipenser sinensis Gray | 52. Coreius septentrionalis (Nichols) |
| 6. Huso dauricus (Georgi) | 53. Platysmacheilus longibarbatus Lo, Yao et Chen |
| 7. Psephurus gladius (Martens) | 54. Schizothorax biddulphi G┨nther |
| 8. Macrura reevesi (Richardson) | 55. Schizothorax taliensis Regan |
| SALMONS: 9-15 | 56. Aspiorhynchus laticeps (Day) |
| 9. Oncorhynchus masou formosanus (Jordan et Oshima) | 57. Diptychus kaznakovi (Nichosky) |
| 10. Hucho taimen (Pallas) | 58. Oxygymnocypris stewartii (Lloyd) |
| 11. Hucho bleekeri Kimura | 59. Chuanchia labiosa Herzenstein |
| 12. Brachymystax lenok tsinlingensis Li | 60. Platypharodon extremus Herzenstein |
| 13. Stenodus leucichthys nelma (Pallas) | 61. Puntioplites proctozysron (Bleeker) |
| 14. Coregonus ussuriensis Berg | 62. Procypris merus Lin |
| 15. Thymallus arcticus grubei Dybowsky | 63. Procypris rabaudi (Tchang) |
| 16. Plecoglossus altivelis Temminck et Schlegel | 64. Cyprinus micristius Regan |
|
17. Anguilla marmorata Quoy et Gaimard |
65. Cyprinus yilongensis Yang et al. |
| 18. Gyrinocheilus aymonieri (Tirant) | 66. Cyprinus megalophthalmus Wu et al. |
| SUCKER: 19 | 67. Cyprinus longipectoralis Chen et Hwang |
| 19. Myxocyprinus asiaticus (Bleeker) | 68. Cyprinus pellegrini Tchang |
| CYPRINID: 20-71 | 69. Cyprinus yunnanensis Tchang |
| 20. Candidia barbutus (Regan) | 70. Cyprinus ilishaestomus Chen et Hwang |
| 21. Parazacco spilurus (G┨nther) | 71. Gobiobotia homalopteroidea Rendahl |
| 22. Zacco chengdui Kimura | 72. Psilorhynchus homaloptera Hora et Mukerji |
| 23. Tanichthys albonubes Lin | COBITID: 73-76 |
| 24. Aphyocypris pooni Lin | 73. Oreonectes anophthalmus Zheng |
| 25 Gobiocypris rarus Ye et Fu | 74. Noemacheilus gejiuensis (Chu et Chen) |
| 26. Luciobrama macrocephalus (Lacepede) | 75. Triplophysa siluroides (Herzenstein) |
| 27. Leuciscus merzbacheri (Zugmayer) | 76. Leptobotia elongata (Bleeker) |
| 28. Atrilinea roulei (Wu) | 77. Plesiomyzon baotingensis Zheng et Chen |
| 29. Macrochirichthys macrochirius (Cuvier et Valenciennes) | 78. Protomyzon pachycheilus Chen |
| 30. Rasborinus formosae Oshima | CATFISHES: 79-89 |
| 31. Pogobrama barbatula (Luo et Huang) | 79. Silurus soldatovi Nikolsky et Soin |
| 32. Anabarilius alburnops (Regan) | 80. Silurus mento Regan |
| 33. Hainania serrata Koller | 81. Kryptopterus moorei Smith |
| 34. Xenocypris yunnanensis Nichols | 82. Sinopangasius semicuitratus Chang et Wu |
| 35. Xenocyprinoides parvulus Chen | 83. Pangasius sanitwangsei Smith |
| 36. Hampala macrolepidota van Hasselt | 84. Cranoglanis bouderius (Richardson) |
| 37. Sinocyclocheilus grahami (Regan) | 85. Akysis brachybarbatus Chen |
| 38. Sinocyclocheilus anophthalmua Chen et Chu | 86. Pseudobagrus madianalis (Regan) |
| 39. Typhlobarbus nudiventris Chu et Chen | 87. Liobagrus kingi Tchang |
| 40. Luciocyprinus langsori Vaillant | 88. Bagarius bagarius (Hamilton) |
| 41. Cosmochilus cardinalis Chu et Roberts | 89. Gagata cenia (Hamilton) |
| 42. Scaphesthes alticorpus Oshima | 90. Coresiniperca roulei (Wu) |
| 43. Parator zonatus (Lin) | 91. Trichogaster trichopterus (Pallas) |
| 44. Balantiocheilus hekouensis Wu | 92. Trachidermus fasciatus Heckel |
| 45. Epalzeorhynchus bicornis Wu |
II. Causes of endangerment of the freshwater fishes in China
1. Alteration of fish habitat
Although there may be many different reasons for endangerment of species of flora and fauna, the most conspicuous reason is the change and loss of habitat for living things. For the fishes, the main factors of endangerment are changes of environment caused by the construction of hydroelectric projects, excessive exploitation of fishery resources, pollution of water systems, unchecked introduction of non-native fish species, and incomplete regulation of the sustainable yield of fisheries (Walter et al. 1993).
1.1 The construction of water conservation projects (the dams of hydroelectric projects)
After construction of hydroelectirc dams, the natural environment of rivers changes enormously. The changes caused by the dams form many stress for fishes, so that they can not adapt to the new conditions. For example, after the construction of dams, running water habitats are changed to those of still water. As a result, running water fishes can not survive. The most serious effect of dam-building to fishes is the change of their reproductive environment. Also, dams can cut off the migration routes of fishes, which in turn directly effects their growth and reproduction, and limits the distribution of their population. In turn, these effects severely compromise the genetic resources of species.
Recently in China, for the purpose of hydroelectric power and irrigation, many dams are being built in stems and branches of rivers. For example, on the Changjiang River, the Gezhouba dam and the Three-gorges dam are in the process of being built. These projects will certainly change the fish habitat and deeply influence the structure of the fish populations and their reproduction. The reproduction and growth of the Chinese sturgeon was deeply influenced by these projects.
1.2 The reclaiming of land from lakes and rivers
The reduction of the area of rivers and lakes is the main problem for the preservation of fish populations in China recently. Human economic activity greatly increases the requirement for grains. For this purpose, people build dikes on the rivers and lakes. The dike-building eliminates shallow areas of rivers and lakes. This action results in reduction of the living space for fishes and other aquatic life. Fish populations also are reduced greatly. These projects are often built around lakes, so that they are more harmful to lake fishes.
1.3 Natural catastrophe
Natural catastrophes may also be one of the reasons for environmental changes. Destruction of forest and vegetation often causes mountain torrents in the upper reaches of rivers, and the floods can carry great amounts of soil and sands into rivers. This errosion must directly influence the fish respiration. This condition often causes the death of great number of fishes.
2. Environmental damage influencing reproduction and food resources
The construction of dams often causes damage to or the disappearance of fish spawning areas in rivers. Because most river fishes have a fixed spawning area, if a dam cuts off river current, their spawning area is inevitably damaged or relocated. Also, pollution caused by industry and other sources can cause damage to fish spawning areas. This condition must limit significantly the reproduction and stability of fish populations. Damage to water plants which are essential in the diet of fishes may further negatively influence the habitat and ability to reproduce of fishes. At the same time, the population of plant-eating fishes may decrease or disappear.
3. Excessive exploitation of fish resources
3.1 The excessive fishery
The increase of the human
population results in the need for increased production of food. As a result,
fish have frequently been over-exploited as food. Such non-sustainable harvesting
is one of the very important reasons for the decline of freshwater fishes in
China. Excessive exploitation has greatly reduced fish populations in all Chinese
rivers and lakes. Many fishes which formerly had economic status have become
rare species or endangered. Examples are Macrura reevesi (Richardson)
and Trachidermus fasiatus Heckel. Because of overexploitation of the
fishery in earlier times, now in the Changjiang River the production of economic
fishes has been decreased to a very small scale. In addition, the number of
professional fishman has decreased greatly because there are not enough commerically
available fishes in the Changjiang River.
3.2 Unchecked elimination of carnivorous fishes from lakes
For the purpose of aquaculture in lakes, people have often removed all carnivorous fishes from lakes. This method sometimes can increase fish production in the short term, but it can also damage the biodiversity and ecosystem of lakes. The result is fewer fish species, and fish populations that are of small-size and young-aged individuals in lakes. Elopichthys bambusa and Erythriculterid are often removed from fish-farming areas, but at the same time, other different species also are eliminated.
3.3 Mass capture of fishes
This fishery technique includes the capture of a mass of parent, juvenile, larva and overwintering fishes. Recently, this harmful fishery technique has become more and more widely used. Unchecked capture of all-aged fishes often influences the balance of fish populations, and this obstructs the replenishment of fry. The result is a greatly decreased population of fishes.
3.4 Special fishery techniques
Some current fishery techniques used in rivers and lakes catch all-sized and all-aged fishes, including the larva and juvenile fishes. These fishery techniques seriously limit the development of fish populations and fatally damage native fish resources. Some water birds and otters are often used as the tools of the fishery, and these animals often catch fishes of any small size, especially the juvenile and larva.
4. Pollution of aquatic environment
Along with the development of industry, agriculture and capital construction,
more and more industrial wastes and farm chemicals are being poured into rivers
and lakes. This pollution directly influences the respiration of fishes. These
wastes seriously pollute the aquatic environment for fishes, so that the living
space of fishes becomes smaller and smaller.
5. Unchecked introduction of non-native
fish species
Introduction of non-native
fishes often causes damage to the balance among fishes in the same water system.
At times the introduced and native species may occupy the same ecological niche.
This condition often results in the extinction of endemic species. Some introduced
fish species have more powerful adaptive capacity. They can occupy all of the
niche so that the endemic species is unable to obtain sufficient living space
and food. The typical example is that of the introduction of perch (Perca
fluviatilis Linnaeus) from the Erqisi River into the Bosten River. This
introduction led to the extinction of the schizothoracin (Aspiorhynchus laticeps
(Day)).
6. Legal problems
In China, there are many regulations
for the protection of fish resources. Also, there are many which limit the exploitation
of a fishery. In reality, however, the execution of these regulations is very
difficult in some areas. To change this condition, public relation propaganda
and education are necessary.