**2. Fish distribution and endemism**

#### **2.1 Description of river reaches**

The Yangtze River basin covers an area of about 1.8 million km2 and lies across the three large topographic platforms of the Chinese mainland (Fig. 1). The riverhead is located on the Tibetan plateau, where the mean elevation is over 4500 m (Zeng, 1990). Upstream from Yichang (in Hubei Province) is the upper reach, with a narrow valley and a rocky channel of high gradient ratio. The length is more than 4300 km, and the drainage area is almost 100×104 km2. The famous Three Gorges Dam is located in the upper mainstream. The range of the middle reach is from Yichang to Hukou (in Jiangxi Province), with a length of about 950 km and a drainage area of almost 68×104 km2. Here, the river has a gentle gradient and takes a meandering course. It connects with shallow lakes of various sizes and numerous tributaries and forms an endemic Chinese compound ecosystem of inland water. From

Fig. 1. Sketch map of the Yangtze River basin

Hukou downward to the mouth of the river is the lower reach, with a length of about 930 km. The drainage area is about 12×104 km2. This segment of the river wanders among plains and hills, and several large interior lakes, such as Lake Caohu and Lake Taihu in association with many tributaries, drain into the reach (Chen et al., 2000). In the estuary confluent with the East China Sea, the river forms a trumpet shaped delta.

#### **2.2 Faunal composition**

42 Ecosystems Biodiversity

biological and biogeographical aspects. In the present chapter, we collected and synthesized these scattered data from relevant literature including Chu (1955), Du (1962), Anonymous (1976, 1980), Yang (1987), Zeng (1990), Zhang (1991), Wu & Wu (1992), Ding (1994), Huang & Xie (1996), Chen (1998), Yue & Chen (1998), Li et al. (1998), Chu et al. (1999), Song et al. (1999), Yue (2000), Ni & Zhu (2005), Xie & Yang (2005), Zhuang et al. (2006), Ye et al. (2006; 2007), Ye (2007), Zhang & Li (2007), Wu & Zhong (2008), Zhang et al. (2008). Threatened status of fish species in the Yangtze River basin was compiled from China Species Red List (Wang & Xie, 2009) and China Red Data Book of Endangered Animals (Yue & Chen, 1998) into five threatened categories: extinct (EX), extinct in the wild (EW), critically endangered (CR), endangered (EN) and vulnerable (VU). Our main purposes were (1) to investigate large-scale distribution and endemic species composition of fishes in different reaches of the Yangtze River basin, (2) to rank the major threats to impaired or extinct fish species and quantify the relative contribution of intrinsic factors to fish endangerment, and (3) to provide recommendations for fish biodiversity conservation in the Yangtze River basin.

The Yangtze River basin covers an area of about 1.8 million km2 and lies across the three large topographic platforms of the Chinese mainland (Fig. 1). The riverhead is located on the Tibetan plateau, where the mean elevation is over 4500 m (Zeng, 1990). Upstream from Yichang (in Hubei Province) is the upper reach, with a narrow valley and a rocky channel of high gradient ratio. The length is more than 4300 km, and the drainage area is almost 100×104 km2. The famous Three Gorges Dam is located in the upper mainstream. The range of the middle reach is from Yichang to Hukou (in Jiangxi Province), with a length of about 950 km and a drainage area of almost 68×104 km2. Here, the river has a gentle gradient and takes a meandering course. It connects with shallow lakes of various sizes and numerous tributaries and forms an endemic Chinese compound ecosystem of inland water. From

**2. Fish distribution and endemism** 

Fig. 1. Sketch map of the Yangtze River basin

**2.1 Description of river reaches** 

Our synthesis (see Appendix 1) showed that there are 416 fish species and subspecies (16 orders and 33 families) known from the entire Yangtze River basin, which amount to about 40% of the total freshwater fishes in China (Zhu, 1995) and far exceed the number of any other river systems in China. For example, the Pearl River has 294 and the Yellow River only has 150 fish species and subspecies (Cao, 1992). Of these fishes in the Yangtze River basin, 362 species and subspecies spend all their lives in fresh water (Table 1), and 11 species of migratory fishes include eight anadromous species (*Acipenser sinensis*, *Macrura reevesi*, *Coilia ectenes*, *C. mystus*, *Myxocyprinus asiaticus*, *Hemisalanx prognathus*, *Takifugu obscurus*, *T. flavidus*) and three catadromous species (*Anguilla japonica*, *A. marmorata*, *Trachidermus fasciatus*). The rest 43 species chiefly live in the brackish water of the estuary with a wide range of salt tolerance, moving regularly between coasts and the estuary. A significant feature of the fish fauna in the Yangtze River basin is the large amount of endemic fishes (Table 1). There are 178 endemic species that occupy 42.8% of the total number of fishes in the basin.


a Data are cited from Nelson (2006). b Freshwater species plus those species frequently occurring in freshwater that may otherwise be diadromous or simply entering fresh water in substantial numbers or in a substantial portion of their range.

Table 1. Species number of fishes in the Yangtze River basin and in the world

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 45

(Cyprinidae) are two genera with the highest species numbers in the basin, accounting for 6.5 and 4.1% of the total species, and 8.4 and 9.0% of the total endemic species, respectively (see Appendix 1). Tectonic activities, such as uplift of the Tibetan Plateau, were believed to be important and responsible for the higher diversity of the two genera (Cao et al., 1981). Tectonic activity has also been associated with the large numbers of endemic species in

The fishes are not evenly distributed in the Yangtze River basin (Fig. 4). Among the 416 species, 206 species occupy only one of the five defined areas of the basin (riverhead, upper reach, middle reach, lower reach, and estuary). Common species that occur in two, three or four of the defined areas are all less than 25% of the total fish species number in the basin. Endemic fishes appear to have the similar distribution pattern. Only four endemic species (*Squalidus nitens*, *Saurogobio gymnocheilus*, *Parabotia bimaculata*, and *Pelteobagrus eupogon*) are common to the three reaches and estuary. Most of the 178 endemic fishes (116 species) occupy one of the define areas. In particular, 97 endemic species were found only in the upper reach (Table 2), indicating that the distribution of the endemic fishes intensively

> 12345 Fish occurrence from the five defined areas of the river

In the riverhead waters, the number of fishes is very small, including five cyprinid fishes, seven species of genus Triplophysa, and two species of family Sisoridae (see Appendix 1). Here, the mean elevation is over 4500 m (Zeng, 1990) and only some specialists could live. Of these fishes, five species were found only in the riverhead (Table 1) and the other nine species were also reported in the upper reach. Nearly 60% species are endemic fishes, and

one species (*Triplophysa tanggulaensis*) was recorded only in the riverhead (Table 2).

All fishes Endemic fishes

other river basins (Minckley et al., 1986).

**2.3 Large-scale distribution** 

occurs there.

0

Fig. 4. Distribution range of fishes in the Yangtze River basin

50

100

150

Species number

200

250

The most species-rich order in the Yangtze River basin is Cypriniformes (Table 1), for which the proportion of species number in the basin to those in the world is 8.6%. And there are four orders (Mugiliformes, Tetraodontiformes, Pleuronectiformes, Acipenseriformes) for which the proportion of number of species using freshwater in the basin to those in the world is more than 10%. This indicates that fish biodiversity in the Yangtze River basin plays an important role in the freshwater fish species bank of the world.

Cyprinidae, Cobitidae, Gobiidae, Bagridae and Homalopteridae are the most species- or endemic species-rich families (Fig. 2 and 3). Triplophysa (Cobitidae) and Schizothorax

Fig. 2. Percentage of species number of the most species-rich families to the total species in the Yangtze River basin

Fig. 3. Percentage of endemic species number of each family to the total endemic species in the Yangtze River basin

(Cyprinidae) are two genera with the highest species numbers in the basin, accounting for 6.5 and 4.1% of the total species, and 8.4 and 9.0% of the total endemic species, respectively (see Appendix 1). Tectonic activities, such as uplift of the Tibetan Plateau, were believed to be important and responsible for the higher diversity of the two genera (Cao et al., 1981). Tectonic activity has also been associated with the large numbers of endemic species in other river basins (Minckley et al., 1986).

#### **2.3 Large-scale distribution**

44 Ecosystems Biodiversity

The most species-rich order in the Yangtze River basin is Cypriniformes (Table 1), for which the proportion of species number in the basin to those in the world is 8.6%. And there are four orders (Mugiliformes, Tetraodontiformes, Pleuronectiformes, Acipenseriformes) for which the proportion of number of species using freshwater in the basin to those in the world is more than 10%. This indicates that fish biodiversity in the Yangtze River basin

Cyprinidae, Cobitidae, Gobiidae, Bagridae and Homalopteridae are the most species- or endemic species-rich families (Fig. 2 and 3). Triplophysa (Cobitidae) and Schizothorax

> Other families, 6.01%

> > Cyprinidae, 46.88%

Cyprinidae, 56.18%

Mastacembelidae , 0.72%

Cobitidae, 15.63%

Salmonidae, 0.56% 0.56%

Fig. 2. Percentage of species number of the most species-rich families to the total species in

Tetrodontidae,

Fig. 3. Percentage of endemic species number of each family to the total endemic species in

Acipenseridae, 0.56%

plays an important role in the freshwater fish species bank of the world.

Channidae, 0.72%

Gobiidae , 6.25%

Gobiidae , 2.25%

Salangidae, 0.56%

Eleotridae , 1.20% Mugilidae, 0.96%

Cynoglossidae , 0.96%

Serranidae, 1.92% Salangidae, 1.92% Sisoridae , 2.16%

Siluridae, 2.16%

Tetrodontidae, 2.88% Homalopteridae, 4.57% Bagridae, 5.05%

Cobitidae, 20.22%

Homalopteridae, 7.87%

Bagridae, 3.93% Sisoridae , 3.93% Siluridae, 3.37%

the Yangtze River basin

the Yangtze River basin

The fishes are not evenly distributed in the Yangtze River basin (Fig. 4). Among the 416 species, 206 species occupy only one of the five defined areas of the basin (riverhead, upper reach, middle reach, lower reach, and estuary). Common species that occur in two, three or four of the defined areas are all less than 25% of the total fish species number in the basin. Endemic fishes appear to have the similar distribution pattern. Only four endemic species (*Squalidus nitens*, *Saurogobio gymnocheilus*, *Parabotia bimaculata*, and *Pelteobagrus eupogon*) are common to the three reaches and estuary. Most of the 178 endemic fishes (116 species) occupy one of the define areas. In particular, 97 endemic species were found only in the upper reach (Table 2), indicating that the distribution of the endemic fishes intensively occurs there.

Fig. 4. Distribution range of fishes in the Yangtze River basin

In the riverhead waters, the number of fishes is very small, including five cyprinid fishes, seven species of genus Triplophysa, and two species of family Sisoridae (see Appendix 1). Here, the mean elevation is over 4500 m (Zeng, 1990) and only some specialists could live. Of these fishes, five species were found only in the riverhead (Table 1) and the other nine species were also reported in the upper reach. Nearly 60% species are endemic fishes, and one species (*Triplophysa tanggulaensis*) was recorded only in the riverhead (Table 2).

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 47

body lengths of crucian carp (*Carassius auratus auratus*), sneakhead fish (*Channa argus*), redfin culter (*Cultrichthys erythropterus*), and Chinese perch (*Siniperca chuatsi*) have shown a remarkable decline (Table 4). Extensive fishing might have removed more fast-growing

MS RS LS PS

before 1971 67 9 (13.4%) 9 (13.4%) 49 (73.2%) 5.22% Huang & Xie, 1996 1992-1994 39 5 (12.8%) 3 (7.7%) 31 (79.5%) 0.26% Huang & Xie, 1996

1959 64 8 (12.5%) 12 (18.8%) 44 (68.7%) 10.0% Song et al., 1999 1992 57 4 (7.0%) 12 (21.1%) 41 (71.9%) 5.0% Song et al., 1999

1997-1999 58 6 (10.3%) 4 (6.9%) 48 (82.8%) 9.4% Xie & Yang, 2005

before 1980 117 14 (12.0%) 32 (27.4%) 71 (60.7%) - Zhang & Li, 2007 1997-2000 101 7 (6.9%) 24 (23.8%) 70 (69.3%) - Zhang & Li, 2007

Age

1234

1960 61 118 184 231 Anonymous, 1976 1988 38 63 83 99 Zhang, 1991

1998 198 305 366 443 Xie & Yang, 2005

1958 115 159 218 235 Anonymous, 1976 2006 131 148 176 191 Zhang et al., 2008

1959 177 246 335 425 Anonymous, 1976 1997 131 247 310 349 Li et al., 1998

1959 173 220 324 - Anonymous, 1976 1997 127 228 289 328 Li et al., 1998

Reference

Before 1974 72 10 (13.9%) 14 (19.4%) 48 (66.7%) 11.4% Ye, 2007

SR: Species richness; MS: Number and percentage of migratory species in fish community; RS: Number and percentage of riverine species in fish community; LS: Number and percentage of limnicolous

Lake Year SR Ecological group of fishes Reference

individuals and thus left more stunted individuals (Cao et al., 1991).

species in fish community; PS: Percentage of piscivorous species in fish catches.

Fish species Lake Year

*auratus* Lake Honghu

*erythropterus* Lake Poyang

(Female) Lake Poyang

*Siniperca chuatsi* (Male) Lake Poyang

in lakes of the Yangtze River basin

**3.2 Species endangerment** 

Table 3. Historical changes of fish community structure in Yangtze River's lakes

*Channa argus* Lake Liangzi 1956 190 288 398 516 Du, 1962

Table 4. Historical changes of age-specific body lengths (standard length, unit: mm) of fishes

It was estimated that at least 20% of the world's freshwater fish species were seriously threatened or extinct, mainly as a result of habitat modification (competition for water, drainage, and pollution), species introduction, and commercial exploitation (Groombridge,

Lake Donghu

Lake Honghu

Lake Liangzi

Lake Poyang

*Carassius auratus* 

*Cultrichthys* 

*Siniperca chuatsi* 

The upper reach has the highest species number, and more than half species are endemic (Table 2). There are 279 species and subspecies of fishes from a wide range of taxonomic categories. Taking food of adhering algae and invertebrates, most of them adapt to rapid current and inhabit the underlayer, while others (fishes of families Homalopteridae and Sisoridae) adhere to and climb on the stones of the riverbed. The Chinese paddlefish (*Psephurus gladius*) and Chinese sucker (*Myxocyprinus asiaticus*), which are distributed mainly in the Yangtze River and could be found in all of the three reaches and their main branches, at present occur chiefly in the upper reach. There were only two migratory fishes, but the Japanese eel (*Anguilla japonica*) disappeared after the Gezhouba Dam was constructed in the upper mainstream (Xie & Chen, 1999).

Fishes in the middle and lower reaches are also abundant, but with lower proportion of endemic fishes compared with the upper reach (Table 2). More migratory fishes (*Anguilla marmorata, Macrcura reevesi, Coilia ectenes, C. mystus, Myxocyprinus asiaticus, Hemisalanx prognathus, Trachidermus fasciatus, Takifugu obscurus, T. flavidus*) occur in the middle and lower reaches. Some euryhaline marine fishes inhabit the lower reach and the estuary of the river, such as *Neosalanx andersoni*, *Liza carinatus*, *Mugil cephalus*, *Terapon jarbua*, *Repomucenus olidus*, *Cynoglossus gracilis*, *and Takifugu spp*.


Note: The number in parentheses indicates the number of fish species found only in that area.

Table 2. Species number of fishes in different areas of the Yangtze River basin

#### **3. Threats to fish biodiversity**

#### **3.1 Structural change of fish community**

Historical variations in the fish community of Yangtze River's lakes can be summarized as follows: (1) decline in species richness and number of migratory species; (2) decrease in the abundance of piscivorous species in fish catches; and (3) diminution in age-specific body length of commercial fishes (Cao et al., 1991; Xie & Chen, 1999).

Here, four examples from Lake Donghu, Lake Honghu, Lake Liangzi and Lake Poyang illustrated the changes of species richness, ecological and trophic structures of fish community during the past half century (Table 3). Apparent reduction of species richness was observed in these lakes, especially a sharp decline in Lake Donghu that is a typical urban lake and therefore received more disturbances from human being. The number and percentage of migratory fishes decreased in all the four lakes, mainly due to river-lake blockage by the building of sluice gates. The comparison of fish catches indicated that the proportion of piscivorous fishes tended to decrease dramatically, mainly due to their relatively high vulnerability to over-fishing and habitat destruction or degradation.

Another five examples on four commercial fish species were used to demonstrate the size diminution of fishes in the Yangtze River's lakes. During the past decades, the age-specific body lengths of crucian carp (*Carassius auratus auratus*), sneakhead fish (*Channa argus*), redfin culter (*Cultrichthys erythropterus*), and Chinese perch (*Siniperca chuatsi*) have shown a remarkable decline (Table 4). Extensive fishing might have removed more fast-growing individuals and thus left more stunted individuals (Cao et al., 1991).


SR: Species richness; MS: Number and percentage of migratory species in fish community; RS: Number and percentage of riverine species in fish community; LS: Number and percentage of limnicolous species in fish community; PS: Percentage of piscivorous species in fish catches.



Table 4. Historical changes of age-specific body lengths (standard length, unit: mm) of fishes in lakes of the Yangtze River basin

#### **3.2 Species endangerment**

46 Ecosystems Biodiversity

The upper reach has the highest species number, and more than half species are endemic (Table 2). There are 279 species and subspecies of fishes from a wide range of taxonomic categories. Taking food of adhering algae and invertebrates, most of them adapt to rapid current and inhabit the underlayer, while others (fishes of families Homalopteridae and Sisoridae) adhere to and climb on the stones of the riverbed. The Chinese paddlefish (*Psephurus gladius*) and Chinese sucker (*Myxocyprinus asiaticus*), which are distributed mainly in the Yangtze River and could be found in all of the three reaches and their main branches, at present occur chiefly in the upper reach. There were only two migratory fishes, but the Japanese eel (*Anguilla japonica*) disappeared after the Gezhouba Dam was

Fishes in the middle and lower reaches are also abundant, but with lower proportion of endemic fishes compared with the upper reach (Table 2). More migratory fishes (*Anguilla marmorata, Macrcura reevesi, Coilia ectenes, C. mystus, Myxocyprinus asiaticus, Hemisalanx prognathus, Trachidermus fasciatus, Takifugu obscurus, T. flavidus*) occur in the middle and lower reaches. Some euryhaline marine fishes inhabit the lower reach and the estuary of the river, such as *Neosalanx andersoni*, *Liza carinatus*, *Mugil cephalus*, *Terapon jarbua*, *Repomucenus* 

Riverhead 14 (5) 8 (1) 57.1 Upper reach 279 (119) 147 (97) 52.7 Middle reach 227 (36) 70 (17) 30.8 Lower reach 158 (5) 23 (1) 14.6 Estuary 142 (41) 10 (0) 7.0 Note: The number in parentheses indicates the number of fish species found only in that area. Table 2. Species number of fishes in different areas of the Yangtze River basin

Historical variations in the fish community of Yangtze River's lakes can be summarized as follows: (1) decline in species richness and number of migratory species; (2) decrease in the abundance of piscivorous species in fish catches; and (3) diminution in age-specific body

Here, four examples from Lake Donghu, Lake Honghu, Lake Liangzi and Lake Poyang illustrated the changes of species richness, ecological and trophic structures of fish community during the past half century (Table 3). Apparent reduction of species richness was observed in these lakes, especially a sharp decline in Lake Donghu that is a typical urban lake and therefore received more disturbances from human being. The number and percentage of migratory fishes decreased in all the four lakes, mainly due to river-lake blockage by the building of sluice gates. The comparison of fish catches indicated that the proportion of piscivorous fishes tended to decrease dramatically, mainly due to their

Another five examples on four commercial fish species were used to demonstrate the size diminution of fishes in the Yangtze River's lakes. During the past decades, the age-specific

relatively high vulnerability to over-fishing and habitat destruction or degradation.

All fishes (A) Endemic fishes (E) E/A (%)

constructed in the upper mainstream (Xie & Chen, 1999).

*olidus*, *Cynoglossus gracilis*, *and Takifugu spp*.

**3. Threats to fish biodiversity** 

**3.1 Structural change of fish community** 

length of commercial fishes (Cao et al., 1991; Xie & Chen, 1999).

It was estimated that at least 20% of the world's freshwater fish species were seriously threatened or extinct, mainly as a result of habitat modification (competition for water, drainage, and pollution), species introduction, and commercial exploitation (Groombridge,

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 49

destruction. We tabulated the number of species threatened by four broad categories of threats: habitat loss/degradation, unreasonable harvesting, water pollution, and biological invasion. We then used the resulting database to determine the frequency of the threat categories and intrinsic factors (i.e. recruitment/reproduction, juvenile mortality, population density, growth rate, and dispersal range) for the threatened fish species. We further subdivided primary threat factors into finer categories, and determined the

Fig. 5 presents a summary of the percentages of fish species in the Yangtze River basin imperilled by the major threats. Unreasonable harvesting is the most pervasive threat to the fishes in the Yangtze River basin, contributing to the endangerment of 86.2% of the listed species, followed by habitat loss/degradation (43.1%), water pollution (30.8%), and biological invasion (27.7%). In particular, overfishing (83.1%) was identifies as the most severe threat. The great frequency of overfishing stems mainly from China's large and poor population, along with widespread trade in fishery products. The use of devastating fishing methods, such as ever-finer meshed nets, poisons, explosives, and electric shocking, is also a contributing factor. Within the threats to habitat loss/degradation, damming and other hydraulic construction appeared to be the most significant threat. The construction of dams at cascades in the river and its tributaries has blocked the passage of migratory fish species, changed hydrological conditions, made their habitats fragmented, and brought about severe impacts on fish habitats and spawning environments. Water pollution influences fish resources not only through direct effects on fish survival, but also through negative impacts on various kinds of food organisms for fishes such as plankton and benthos, resulting in

Invasion of non-indigenous species is also a serious threat to biodiversity in the basin. Fish compositions in some plateau lakes of the upper Yangtze River, such as Lake Dianchi and Lake Lugu, have been seriously affected by exotic species introductions (Xie et al., 2001). Exotic species compete with native fishes for food and other resources, leading to greatly reduced numbers of local species, and even the local extinction of some species (Chen et al., 1998). The number of native species of Lake Dianchi has declined from 25 in the 1940s, to 15 in 1978, and 8 in 1982. A recent fish fauna investigation conducted in the lake found only five native species, and the number of endemic species and subspecies had declined from

Among the intrinsic factors we analyzed, limited dispersal and restricted range appear to have the highest contributions to the effects of the threats upon fishes in the river basin (Fig. 6). The other intrinsic factors lag behind these two primary factors in terms of their frequency for the imperilled and extinct fish species (Fig. 6). In comparison, the three factors (slow growth rate, population fluctuation, and high juvenile mortality) could be minor

The endemic fish distribution in the upper reach is represented by complicated assemblages, which are highly correlated to the topographic and geomorphic characteristics of the upper Yangtze River basin (He et al., 2011). Generally, these endemic species are well adapted to specific habitats with relatively small population size. For example, the fishes of Triplophysa and Schizothorax usually live in the tributaries and mountain streams with torrential flows and gravel riverbeds, whose origin, evolution and distribution are related to the uplift of the Tibetan Plateau (Cao et al., 1981). They are usually sensitive to environmental changes or

frequency of each of these causes of endangerment.

decreases in the abundance of natural fish stocks.

nine in the 1950s to two (Xie & Chen, 1999; Xie et al., 2001).

causes of endangerment in the Yangtze River basin.

1992). In the Yangtze River basin, there are 65 threatened fish species included in the China Species Red List (Wang & Xie, 2009), belonging to 10 orders and 18 families (see Appendix 1). These fishes are classified into five threatened categories (Table 5), i.e., extinct (two species), extinct in the wild (two species), critically endangered (five species), endangered (36 species), and vulnerable (20 species). It should be noted that 69% of the threatened or extinct fishes are endemic species in the Yangtze River basin (Table 5).

As shown in Table 6, the two species extinct in the wild (*Anabarilius polylepis* and *Schizothorax parvus*) and one extinct species (*Anabarilius liui liui*) were known to be endemic only in the upper reach. Another extinct species (*Atrilinea macrolepis*) was endemic only in the middle reach. Of the five critically endangered species, Chinese paddlefish (*Psephurus gladius*) were recorded in the upper, middle, lower reaches and estuary, and *Euchiloglanis kishinouyei* were recorded in both riverhead and upper reach. The other three critically endangered species (*Megalobrama elongata*, *Schizothorax longibarbus*, and *Leiocassis longibarbus*) occurred only in the upper reach. Overall, there are much more threatened or extinct fish species distributed in the middle reach than in the other areas of the Yangtze River basin.


Table 5. Species number of fishes in different threatened categories


Table 6. Threatened status of fishes in different areas of the Yangtze River basin

#### **3.3 Major threats**

From the China Species Red List (Wang & Xie, 2009) and China Red Data Book of Endangered Animals (Yue & Chen, 1998), we extracted the recognized causes (major threats and intrinsic factors) of endangerment or extinction of the 65 species in the Yangtze River basin. We did not try to distinguish between ongoing and historical threats, because such information is often lacking, and the distinction itself is problematic in the case of habitat

1992). In the Yangtze River basin, there are 65 threatened fish species included in the China Species Red List (Wang & Xie, 2009), belonging to 10 orders and 18 families (see Appendix 1). These fishes are classified into five threatened categories (Table 5), i.e., extinct (two species), extinct in the wild (two species), critically endangered (five species), endangered (36 species), and vulnerable (20 species). It should be noted that 69% of the threatened or

As shown in Table 6, the two species extinct in the wild (*Anabarilius polylepis* and *Schizothorax parvus*) and one extinct species (*Anabarilius liui liui*) were known to be endemic only in the upper reach. Another extinct species (*Atrilinea macrolepis*) was endemic only in the middle reach. Of the five critically endangered species, Chinese paddlefish (*Psephurus gladius*) were recorded in the upper, middle, lower reaches and estuary, and *Euchiloglanis kishinouyei* were recorded in both riverhead and upper reach. The other three critically endangered species (*Megalobrama elongata*, *Schizothorax longibarbus*, and *Leiocassis longibarbus*) occurred only in the upper reach. Overall, there are much more threatened or extinct fish species distributed in the middle reach than in the other areas of the Yangtze River basin.

Extinct (EX) 2 2 100 Extinct in the wild (EW) 2 2 100 Critically endangered (CR) 5 4 80 Endangered (EN) 36 27 75 Vulnerable (VU) 20 10 50 Total evaluated 65 45 69

Threatened categories

Critically endangered

From the China Species Red List (Wang & Xie, 2009) and China Red Data Book of Endangered Animals (Yue & Chen, 1998), we extracted the recognized causes (major threats and intrinsic factors) of endangerment or extinction of the 65 species in the Yangtze River basin. We did not try to distinguish between ongoing and historical threats, because such information is often lacking, and the distinction itself is problematic in the case of habitat

Riverhead 0 0 1 2 1 4 Upper reach 1 2 5 28 13 48 Middle reach 1 0 1 9 10 20 Lower reach 0 0 1 8 89 Estuary 0 0 1 8 3 12

Table 6. Threatened status of fishes in different areas of the Yangtze River basin

evaluated Extinct Extinct in

Endangered Vulnerable

Table 5. Species number of fishes in different threatened categories

the wild

**3.3 Major threats** 

All species (A) Endemic species (E) E/A (%)

Total

extinct fishes are endemic species in the Yangtze River basin (Table 5).

destruction. We tabulated the number of species threatened by four broad categories of threats: habitat loss/degradation, unreasonable harvesting, water pollution, and biological invasion. We then used the resulting database to determine the frequency of the threat categories and intrinsic factors (i.e. recruitment/reproduction, juvenile mortality, population density, growth rate, and dispersal range) for the threatened fish species. We further subdivided primary threat factors into finer categories, and determined the frequency of each of these causes of endangerment.

Fig. 5 presents a summary of the percentages of fish species in the Yangtze River basin imperilled by the major threats. Unreasonable harvesting is the most pervasive threat to the fishes in the Yangtze River basin, contributing to the endangerment of 86.2% of the listed species, followed by habitat loss/degradation (43.1%), water pollution (30.8%), and biological invasion (27.7%). In particular, overfishing (83.1%) was identifies as the most severe threat. The great frequency of overfishing stems mainly from China's large and poor population, along with widespread trade in fishery products. The use of devastating fishing methods, such as ever-finer meshed nets, poisons, explosives, and electric shocking, is also a contributing factor. Within the threats to habitat loss/degradation, damming and other hydraulic construction appeared to be the most significant threat. The construction of dams at cascades in the river and its tributaries has blocked the passage of migratory fish species, changed hydrological conditions, made their habitats fragmented, and brought about severe impacts on fish habitats and spawning environments. Water pollution influences fish resources not only through direct effects on fish survival, but also through negative impacts on various kinds of food organisms for fishes such as plankton and benthos, resulting in decreases in the abundance of natural fish stocks.

Invasion of non-indigenous species is also a serious threat to biodiversity in the basin. Fish compositions in some plateau lakes of the upper Yangtze River, such as Lake Dianchi and Lake Lugu, have been seriously affected by exotic species introductions (Xie et al., 2001). Exotic species compete with native fishes for food and other resources, leading to greatly reduced numbers of local species, and even the local extinction of some species (Chen et al., 1998). The number of native species of Lake Dianchi has declined from 25 in the 1940s, to 15 in 1978, and 8 in 1982. A recent fish fauna investigation conducted in the lake found only five native species, and the number of endemic species and subspecies had declined from nine in the 1950s to two (Xie & Chen, 1999; Xie et al., 2001).

Among the intrinsic factors we analyzed, limited dispersal and restricted range appear to have the highest contributions to the effects of the threats upon fishes in the river basin (Fig. 6). The other intrinsic factors lag behind these two primary factors in terms of their frequency for the imperilled and extinct fish species (Fig. 6). In comparison, the three factors (slow growth rate, population fluctuation, and high juvenile mortality) could be minor causes of endangerment in the Yangtze River basin.

The endemic fish distribution in the upper reach is represented by complicated assemblages, which are highly correlated to the topographic and geomorphic characteristics of the upper Yangtze River basin (He et al., 2011). Generally, these endemic species are well adapted to specific habitats with relatively small population size. For example, the fishes of Triplophysa and Schizothorax usually live in the tributaries and mountain streams with torrential flows and gravel riverbeds, whose origin, evolution and distribution are related to the uplift of the Tibetan Plateau (Cao et al., 1981). They are usually sensitive to environmental changes or

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 51

Species that use distinct environments during different stages of their life histories (e.g. migratory fish) are at risk from elimination of crucial habitats or erection of structures that impede movement. For example, the Chinese paddlefish (*Psephurus gladius*) declined drastically in the Yangtze River after the Gezhouba Dam blocked access to its upstream spawning habitats, and the fish likely faces extinction (Wei et al., 1997). Furthermore, they are especially vulnerable to overfishing and other environmental hazards because the long maturation time limits rates of population recovery. On the other hand, fragmentation of resident populations also results from barriers, and may ultimately lead to species loss. During the late 1950s-1970s, sluice gates were constructed in almost all lakes of the middle and lower reaches except for Lake Dongting and Lake Poyang for water conservancy projects. The sluice gates blocked interchanges of fishes in the river–lakes ecosystem. Severance of fish exchange has brought about the decline in natural fish stocks in the river and its lakes, especially the decline in species richness and abundance of migratory fishes

Restoration of the Yangtze River to its original state is impractical given the constraints prevailing in the region, but some degree of rehabilitation will be possible if relevant legislation and scientific information are promptly applied. Even though China lacks a truly comprehensive law on nature conservation, it did enact the China Wildlife Protection Law in 1989 to protect rare and endangered species. Although the law has yet to be completely enforced, China has established a legislative framework for biodiversity conservation and a number of action plans have been initiated (Xu et al., 1999). A fishery law dating from 1986 and revised in 2000 proscribes fishing of rare and precious aquatic animals. Within the last two decades, an interprovincial authority, the Administrative Commission of the Yangtze River Fisheries Resources, was established to control illegal fishing activities involving the use of electricity, explosives, and poisons, and to protect fish stocks in the Yangtze River. In February 2003, an annual fishing moratorium of three to six months was introduced to protect 8100 km of the river, including 4090 km of the mainstream and more than 4000 km of its tributaries. This measure builds on the well established and widespread practice of stocking Chinese rivers and lateral lakes with cultured fries of major carp species to maintain or enhance fishery yields (Fu et al., 2003). Such stocking cannot be regarded as a measure that contributes greatly to biodiversity conservation, because it has implications for the genetic variability of indigenous carp species. However, it may reduce harvesting

pressure on endangered species that could benefit from the fishing moratorium.

Problems with protection of endemic fishes and implementation of wildlife protection legislation in the Yangtze River basin exist because the natural resources laws and regulations, especially for fisheries, have been formulated from the standpoint of economic value, which emphasizes utilization rather than protection. Thus the conservation of endangered species is mainly the responsibility of the Ministry of Agriculture, which has the historical remit of increasing or expanding the capture quotas of economically important species. Moreover, a separate authority, the Ministry of Water Resources, has an overlapping responsibility with the Ministry of Agriculture, but it is directed toward maintaining water supplies for human consumption and agriculture, whereas protection of

(Xie & Chen, 1999).

**4. Conservation status and strategies** 

disturbances, and more prone to extinction under the threats of overfishing and habitat loss, mainly due to their limited dispersal and restricted range.

Fig. 5. Rank of the major threats to fish endangerment in the Yangtze River basin

Fig. 6. Rank of the intrinsic factors for fish endangerment in the Yangtze River basin

Species that use distinct environments during different stages of their life histories (e.g. migratory fish) are at risk from elimination of crucial habitats or erection of structures that impede movement. For example, the Chinese paddlefish (*Psephurus gladius*) declined drastically in the Yangtze River after the Gezhouba Dam blocked access to its upstream spawning habitats, and the fish likely faces extinction (Wei et al., 1997). Furthermore, they are especially vulnerable to overfishing and other environmental hazards because the long maturation time limits rates of population recovery. On the other hand, fragmentation of resident populations also results from barriers, and may ultimately lead to species loss. During the late 1950s-1970s, sluice gates were constructed in almost all lakes of the middle and lower reaches except for Lake Dongting and Lake Poyang for water conservancy projects. The sluice gates blocked interchanges of fishes in the river–lakes ecosystem. Severance of fish exchange has brought about the decline in natural fish stocks in the river and its lakes, especially the decline in species richness and abundance of migratory fishes (Xie & Chen, 1999).

#### **4. Conservation status and strategies**

50 Ecosystems Biodiversity

disturbances, and more prone to extinction under the threats of overfishing and habitat loss,

Fig. 5. Rank of the major threats to fish endangerment in the Yangtze River basin

Fig. 6. Rank of the intrinsic factors for fish endangerment in the Yangtze River basin

High juvenile mortality

Population fluctuation

Poor recruitment/reproduction

Slow growth rate

Low density

Restricted range

Limited dispersal

0% 10% 20% 30% 40% 50% 60%

Species affected by threat (percentage)

mainly due to their limited dispersal and restricted range.

Restoration of the Yangtze River to its original state is impractical given the constraints prevailing in the region, but some degree of rehabilitation will be possible if relevant legislation and scientific information are promptly applied. Even though China lacks a truly comprehensive law on nature conservation, it did enact the China Wildlife Protection Law in 1989 to protect rare and endangered species. Although the law has yet to be completely enforced, China has established a legislative framework for biodiversity conservation and a number of action plans have been initiated (Xu et al., 1999). A fishery law dating from 1986 and revised in 2000 proscribes fishing of rare and precious aquatic animals. Within the last two decades, an interprovincial authority, the Administrative Commission of the Yangtze River Fisheries Resources, was established to control illegal fishing activities involving the use of electricity, explosives, and poisons, and to protect fish stocks in the Yangtze River. In February 2003, an annual fishing moratorium of three to six months was introduced to protect 8100 km of the river, including 4090 km of the mainstream and more than 4000 km of its tributaries. This measure builds on the well established and widespread practice of stocking Chinese rivers and lateral lakes with cultured fries of major carp species to maintain or enhance fishery yields (Fu et al., 2003). Such stocking cannot be regarded as a measure that contributes greatly to biodiversity conservation, because it has implications for the genetic variability of indigenous carp species. However, it may reduce harvesting pressure on endangered species that could benefit from the fishing moratorium.

Problems with protection of endemic fishes and implementation of wildlife protection legislation in the Yangtze River basin exist because the natural resources laws and regulations, especially for fisheries, have been formulated from the standpoint of economic value, which emphasizes utilization rather than protection. Thus the conservation of endangered species is mainly the responsibility of the Ministry of Agriculture, which has the historical remit of increasing or expanding the capture quotas of economically important species. Moreover, a separate authority, the Ministry of Water Resources, has an overlapping responsibility with the Ministry of Agriculture, but it is directed toward maintaining water supplies for human consumption and agriculture, whereas protection of

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 53

Conservation must be proactive. Our ability to ameliorate or mitigate the effects of human activities is predicated upon an adequate understanding of river ecology. But information on the prevailing situation with respect to habitat integrity and fish biodiversity in the Yangtze River basin is inadequate. Some published catalogs of fish faunal composition are based on dated literature or old museum collections instead of recent surveys. Information on fish conservation status is thus unreliable, and extinctions may not be evident until long after they have occurred. The basic task of compiling species inventories is one priority for biodiversity conservation, but it should be accompanied by assessments of population size and long-term viability (Dudgeon, 2000). These tasks will require monitoring strategies, such as those developed by Humphrey et al. (1995) in tropical Australia, and formulation of indices of river health that can be applied to individual habitats. Furthermore, explicit information on life histories of endangered species is highly necessary for successful

Data sharing and collaboration between academic institutions and governmental agencies are particularly essential for the effectiveness of fish conservation. All research efforts are in vain if the resulting knowledge is not translated into social and/or political action. This may be the greatest challenge facing conservation ecologists. Ecological stations and networks should be established linking inland water biological laboratories from the universities and the institutions along the Yangtze River, in conjunction with museums, particularly regarding long-term ecological research. This will ensure that currently available information is used effectively. It is also necessary to establish and standardize databases of

The large amount and high endemicity of fish species have resulted in the importance of the Yangtze River basin in the freshwater fish species bank of the world. Fish biodiversity and freshwater ecosystems are seriously jeopardized by human activities in the basin. The decline of diversity and the loss of some fishes will have potential impacts on the global fish biodiversity, so more hotspots of fish biodiversity in the Yangtze River basin should be identified as nature reserves. There is an urgent need for integrated action and legislation to ensure that the endangered species are legally protected within their range. A mixture of strategies will be essential to preserve fish biodiversity in the long term. It must include reserves that protect key, biodiversity-rich water-bodies (e.g. tributaries in the upper reach and river-connecting lakes in the middle reach) and their catchments, as well as species- or habitat-centred plans that reconcile the protection of biodiversity and societal use of water resources. In parallel, conservation ecologists must more effectively communicate the importance and value of fish biodiversity to stakeholders and policy makers, so as to make certain that all available information on fish biodiversity is applied effectively to ensure its

The authors are grateful to the National Science Foundation of China (No. 30900182) and the "Special Fund for Agro-scientific Research in the Public Interest" (No. 200903048-04) for

inland water organisms and associated environmental information.

conservation of the fishes.

**5. Conclusion** 

conservation.

their support.

**6. Acknowledgment** 

water quality is under the jurisdiction of the State Environmental Protection Administration. The conflict between economic development and conservation plus the overlapping and sometimes contradictory responsibilities of government authorities have impeded actions that are needed to preserve biodiversity (Xu et al. 1999). Some progress has been made recently: in 2000, a 400-km section of the upper reach of the Yangtze River was designated as a reserve for rare fishes, but portions of it will be affected by rising water levels behind the Three Gorges Dam and by the dams planned for the Jinsha River tributary. Potential reserve sites for rare fishes elsewhere along the Yangtze River have been identified (Park et al., 2003), but they await official designation.

Since the Yangtze River basin is undergoing a very rapid deterioration as a consequence of human-induced changes, conservation strategies must be improved and expanded. The conservation of the fishes in the upper reach should be considered as a priority. Current knowledge of speciation theories indicates the importance of local processes in generating high endemicity of inland water fauna (Martens, 1997). The high endemicity of fish species in the upper reach indicates that the more immediate conservation need is to retain as many of the natural ecological processes and functions of the river as possible. A conservation recommendation, according to which the habitats rich in endemic species should be identified as the nature reserves, has been put forward (Liu & Cao, 1992). In view of the different endemic fish assemblages (with multiple habitats and different fish compositions) in the upper Yangtze River, different reserves aimed at different conservation objectives should be set up in order to preserve fish biodiversity (He et al., 2011). At present, there are three fish reserves, of which, one is for the protection of rare and unique species in the upper reach at the national level, and two are for the protection of Chinese sturgeon at the provincial level. The National Nature Reserve for Rare and Peculiar Fish Species in the upper Yangtze River is the only national protected zone across many provinces in China. Its management and protection tasks are very arduous. The effective realization of nature reserve functions can be pushed forward only through their tracing, monitoring and appraisal.

In the middle and lower reaches of the Yangtze River basin, the conservation strategies for fishes must take into account the complex life cycles and ontogenetic shifts in habitat requirements of migratory fishes. Restoring the stocks of the migratory fishes should be a priority in these reaches, because the severance between the Yangtze River and its connecting lakes is the most critical factor responsible for the decline of the abundance of the migratory fishes. In addition, fragmentation of the resident population resulting from the severance may ultimately lead to species loss. Ideally, restoration of natural fish stocks in the middle and lower reaches would include restoration of the free flow, so fishes can move freely between the Yangtze River and its lakes. Minimally, construction of a fish passage structure is necessary. Conventional fish ladders designed for salmonids may not be successful because most fishes do not jump. In the basin, there are more than 40 lake-river migratory fishes (species that migrate from lakes to breed in rivers; Liang et al., 1981). Most of them have been affected by severance (Xie & Chen, 1999). Compared to severed lakes, the river-connecting lakes are rich in river-lake migratory fishes (Liang et al., 1981; Liu & Wang, 2010). At present, considering the importance of river-connecting lakes for sustaining populations of the river–lake migratory fishes, river-connecting lakes, such as Lake Dongting and Lake Poyang, are also of high priority for conversation.

Conservation must be proactive. Our ability to ameliorate or mitigate the effects of human activities is predicated upon an adequate understanding of river ecology. But information on the prevailing situation with respect to habitat integrity and fish biodiversity in the Yangtze River basin is inadequate. Some published catalogs of fish faunal composition are based on dated literature or old museum collections instead of recent surveys. Information on fish conservation status is thus unreliable, and extinctions may not be evident until long after they have occurred. The basic task of compiling species inventories is one priority for biodiversity conservation, but it should be accompanied by assessments of population size and long-term viability (Dudgeon, 2000). These tasks will require monitoring strategies, such as those developed by Humphrey et al. (1995) in tropical Australia, and formulation of indices of river health that can be applied to individual habitats. Furthermore, explicit information on life histories of endangered species is highly necessary for successful conservation of the fishes.

Data sharing and collaboration between academic institutions and governmental agencies are particularly essential for the effectiveness of fish conservation. All research efforts are in vain if the resulting knowledge is not translated into social and/or political action. This may be the greatest challenge facing conservation ecologists. Ecological stations and networks should be established linking inland water biological laboratories from the universities and the institutions along the Yangtze River, in conjunction with museums, particularly regarding long-term ecological research. This will ensure that currently available information is used effectively. It is also necessary to establish and standardize databases of inland water organisms and associated environmental information.

#### **5. Conclusion**

52 Ecosystems Biodiversity

water quality is under the jurisdiction of the State Environmental Protection Administration. The conflict between economic development and conservation plus the overlapping and sometimes contradictory responsibilities of government authorities have impeded actions that are needed to preserve biodiversity (Xu et al. 1999). Some progress has been made recently: in 2000, a 400-km section of the upper reach of the Yangtze River was designated as a reserve for rare fishes, but portions of it will be affected by rising water levels behind the Three Gorges Dam and by the dams planned for the Jinsha River tributary. Potential reserve sites for rare fishes elsewhere along the Yangtze River have been identified (Park et al.,

Since the Yangtze River basin is undergoing a very rapid deterioration as a consequence of human-induced changes, conservation strategies must be improved and expanded. The conservation of the fishes in the upper reach should be considered as a priority. Current knowledge of speciation theories indicates the importance of local processes in generating high endemicity of inland water fauna (Martens, 1997). The high endemicity of fish species in the upper reach indicates that the more immediate conservation need is to retain as many of the natural ecological processes and functions of the river as possible. A conservation recommendation, according to which the habitats rich in endemic species should be identified as the nature reserves, has been put forward (Liu & Cao, 1992). In view of the different endemic fish assemblages (with multiple habitats and different fish compositions) in the upper Yangtze River, different reserves aimed at different conservation objectives should be set up in order to preserve fish biodiversity (He et al., 2011). At present, there are three fish reserves, of which, one is for the protection of rare and unique species in the upper reach at the national level, and two are for the protection of Chinese sturgeon at the provincial level. The National Nature Reserve for Rare and Peculiar Fish Species in the upper Yangtze River is the only national protected zone across many provinces in China. Its management and protection tasks are very arduous. The effective realization of nature reserve functions can be pushed forward only through their

In the middle and lower reaches of the Yangtze River basin, the conservation strategies for fishes must take into account the complex life cycles and ontogenetic shifts in habitat requirements of migratory fishes. Restoring the stocks of the migratory fishes should be a priority in these reaches, because the severance between the Yangtze River and its connecting lakes is the most critical factor responsible for the decline of the abundance of the migratory fishes. In addition, fragmentation of the resident population resulting from the severance may ultimately lead to species loss. Ideally, restoration of natural fish stocks in the middle and lower reaches would include restoration of the free flow, so fishes can move freely between the Yangtze River and its lakes. Minimally, construction of a fish passage structure is necessary. Conventional fish ladders designed for salmonids may not be successful because most fishes do not jump. In the basin, there are more than 40 lake-river migratory fishes (species that migrate from lakes to breed in rivers; Liang et al., 1981). Most of them have been affected by severance (Xie & Chen, 1999). Compared to severed lakes, the river-connecting lakes are rich in river-lake migratory fishes (Liang et al., 1981; Liu & Wang, 2010). At present, considering the importance of river-connecting lakes for sustaining populations of the river–lake migratory fishes, river-connecting lakes, such as Lake

Dongting and Lake Poyang, are also of high priority for conversation.

2003), but they await official designation.

tracing, monitoring and appraisal.

The large amount and high endemicity of fish species have resulted in the importance of the Yangtze River basin in the freshwater fish species bank of the world. Fish biodiversity and freshwater ecosystems are seriously jeopardized by human activities in the basin. The decline of diversity and the loss of some fishes will have potential impacts on the global fish biodiversity, so more hotspots of fish biodiversity in the Yangtze River basin should be identified as nature reserves. There is an urgent need for integrated action and legislation to ensure that the endangered species are legally protected within their range. A mixture of strategies will be essential to preserve fish biodiversity in the long term. It must include reserves that protect key, biodiversity-rich water-bodies (e.g. tributaries in the upper reach and river-connecting lakes in the middle reach) and their catchments, as well as species- or habitat-centred plans that reconcile the protection of biodiversity and societal use of water resources. In parallel, conservation ecologists must more effectively communicate the importance and value of fish biodiversity to stakeholders and policy makers, so as to make certain that all available information on fish biodiversity is applied effectively to ensure its conservation.

#### **6. Acknowledgment**

The authors are grateful to the National Science Foundation of China (No. 30900182) and the "Special Fund for Agro-scientific Research in the Public Interest" (No. 200903048-04) for their support.

**Order Family**  *Species*

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 55

*38. Pseudoleubuca sinensis* + + + + *39. P. engraulis* + + + + *40. Toxabramis swinhonis* + + + + *41. Hemiculter leucisculus* + + + +

*43. H. bleekeri* + + + +

*47. Cultrichthys erythropterus* + + + + *48. Culter alburnus* + + + + *49. C. mongolicus mongolicus* + + + +

*52. C. Dabryi* + + + + *53. C. Oxycephalus* + + + + *54. C. oxycephaloides\** + + + *55. Parabramis pekinensis* + + + + *56. Megalobrama skolkovii* + + + +

*58. M. amblycephala\** + + +

*60. Xenocypris argentea* + + + + *61. X. davidi* + + + +

*67. Pseudobrama simony* + + + + *68. Hypophthalmichthys molitrix* + + + + *69. Aristichys nobilis* + + + + *70. Hemibarbus labeo* + + + *71. H. maculates* + + + + *72. H. longirostris* + + *73. Paracanthobrama guichenoti\** + + +

*76. Pseudorasbora parva* + + + + *77. P. elongata* VU + + *78. Sarcocheilichthys sinensis* + + + + *79. S. parvus* + + *80. S. kiangsiensis* + + *81. S. nigripinnis* + + + +

*64. X. microlepis* + + + *65. Distoechodon tumirostris* + + + *66. D. hupeinensis\** EN +

*42. H. tchangi\** +

*50. C. m. elongatus\** + *51. C. m. qionghaiensis\** +

*59. M. elongata\** CR +

*62. X. yunnanensis\** VU + *63. X. fangi\** EN +

*74. Belligobio nummifer* + *75. B. pengxianensis\** EN +

*82. S. davidi\** + *83. Gnathopogon herzensteini\** + + *84. G. imberbis\** + + *85. G. nicholsi\** + +

*44. Hemiculterella sauvagei\** + + *45. H. Wui* + *46. Pseudohemiculter kweichowensis\** +

*57. M. pellegrini\** + +

Threat status

Riverhead

Upper reach Middle reach

Lower reach Estuary


*2. A. sinensis* EN + + + +

*3. Psephurus gladius* CR + + + +

*4. Anguilla japonica* + + + + *5. A. marmorata* EN + +

*6. Macrura reevesi* EN + + +

*7. Coilia ectenes* + + + *8. C. mystus* + +

*9. Myxocyprinus asiaticus* VU + + + +

*10. Zacco platypus* + + + +

*12. Opsariichthys bidens* + + + + *13. Aphyocypris chinensis* + + + +

*18. Mylopharyngodon piceus* + + + + *19. Ctenopharyngodon idellus* + + + + *20. Squaliobarbus curriculus* + + + + *21. Luciobrama macrocephalus* EN + + + + *22. Ochetobius elongatus* + + + + *23. Elopichthys bambusa* + + + +

*15. Phoxinus oxycephalus* + + + *16. Atrilinea roulei* VU + *17. A. macrolepis\** EX +

*32. Sinibrama wui* + + + *33. S. macrops* + + +

*11. Z. chengtui\** VU +

*14. Gobiocypris rarus\** EN +

*24. Anabarilius liui liui\** EX + *25. A. l. chenghaiensis\** + *26. A. brevianalis\** + *27. A. songmingensis\** + *28. A. qionghaiensis\** EN + *29. A. xundianensis\** + *30. A. polylepis\** EW + *31. A. alburnops\** EN +

*34. S. taeniatus\** + *35. Ancherythroculter wangi\** + *36. A. kurematsui\** + *37. A. nigrocauda\** +

*1. Acipenser dabryanus*\* EN + +

**I. Acipenseriformes Acipenseridae**

**Polyodontidae**

**II. Anguilliformes Anguillidae**

**III. Clupeiformes Clupeidae**

**IV. Cypriniformes Catostomidae**

Threat status

Riverhead Upper reach Middle reach

Lower reach Estuary

**Order Family**  *Species*

**Engraulidae** 

**Cyprinidae** 


**Order Family**  *Species*

*134. A. nanchongensis\** 

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 57

*135. Paracheilognathus himantegus* + + + *136. P. imberbis* + + + + *137. Spinibarbus hollandi* + + + *138. S. sinensis\** + + *139. Barbodes laticeps* + *140. B. polylepis\** + *141. Percocyprinus pingi pingi\** VU + *142. Sinocyclocheilus multipunctatus* + *143. S. grahami grahami\** EN + *144. Acrossocheilus labiatus* + *145. A. fascitus* + + *146. A. jishouensis\** + *147. A. monticola\** + + *148. A. elongatus* + *149. A. yunnanensis* + + *150. Onychostoma macrolepis* + + *151. O. sima* + + *152. O. barbata* + + *153. O. lini* VU + *154. O. rara\** EN + + *155. O. angustistomata\** + *156. O. barbata* + + *157. O. daduensis\** + *158. O. brevis\** + *159. Tor brevifilis* + + *160. Sinilabeo rendahli\** + + *161. S. tungting\** + +

*162. S. longibarbatus\** +

*164. R. mutabilis\** + *165. Semilabeo notabilis* VU + *166. Pseudogyrincheilus procheilus\** + + *167. Garra pingi pingi* + + *168. Sinocrossocheilus guizhouensis\** VU + *169. Discogobio yunnanensis* + + *170. D. brachyphysallidos* + *171. Schizothorax (Schizothorax) chongi\** + *172. S. (S.) wangchiachii\** + + *173. S. (S.) dolichonema\** EN + + *174. S. (S.) sinensis\** + + *175. S. (S.) grahami\** VU + *176. S. (S.) cryptolepis\** + *177. S. (S.) heterochilus\** + *178. S. (S.) prenanti\** + + *179. Schizothorax (Racoma) kozlovi\** + *180. S. (R.) yunnanensis weiningensis\** + *181. S. (R.) griseus* EN +

*163. Rectoris luxiensis\** + + +

Threat status

Riverhead

Upper reach Middle reach

Lower reach Estuary


*99. Abbottina rivularis* + + + +

*111. S. gymnocheilus\** + + + +

*115. G. (G.) filifer\** + + +

*120. Rhodeus ocellatus* + + + + *121. R. lighti* + + + + *122. R. fangi* + + + *123. Acheilognathus gracilis\** + + + *124. A. macropterus* + + + +

*126. A. barbatus* + + + + *127. A. barbatulus* + + + +

*129. A. polylepis* + + *130. A. tonkinensis* + + + + *131. A. tabira* + + *132. A. hypselonotus\** + + + *133. A. chankaensis* + + + +

*113. G. (Gobiobotia) tungi* + + *114. G. (G.) meridionalis* +

*101. Microphysogobio fukiensis* + + + *102. M. microstomus\** + *103. M. kiatingensis* + + + *104. M. tungtingensis\** + + *105. Huigobio chenhsinensis* + + *106. Pseudogobio vaillanti* + + + *107. Saurogobio dumerili* + + + *108. S. dabryi* + + + +

*109. S. gracilicaudatus\** + *110. S. xiangjiangensis* +

*116. G. (G.) brevirostris* +

*118. Xenophysogobio boulengeri\** + + *119. X. nudicorpa\** +

*112. Gobiobotia (Progobiobotia) abbreviatea\** +

*125. A. omeiensis\** +

*128. A. elongatus\** EN +

*117. G. (G.) jiangxiensis\** 

*86. G. taeniellus* + *87. Squalidus argentatus* + + + + *88. S. nitens\** + + + + *89. S. wolterstorffi* + + + *90. Coreius heterodon* + + + +

*91. C. guichenoti\** + + *92. Rhinogobio typus* + + + *93. R. hunanensis\** + *94. R. cylindricus\** + + *95. R. ventralis\** + + *96. Platysmacheilus exiguus* + *97. P. longibarbatus\** VU + *98. P. nudiventris\** + +

*100. A. obtusirostris\** +

Threat status

Riverhead Upper reach Middle reach

Lower reach Estuary

**Order Family**  *Species*


**Order Family**  *Species*

*263. S. niulanjiangensis\** 

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 59

*228. T. pseudoscleroptera* + *229. T. robusta* + *230. T. microps* + *231. T. stoliczkae* + *232. T. rotundiventris* + *233. T. ninglangensis\** + *234. T. stenura* + + *235. T. polyfasciata\** + *236. T. angeli\** + *237. T. venusta\** + *238. T. grahami\** + *239. T. xichangensis\** + *240. T. anterodorsalis\** + *241. T. brevicauda* + *242. T. obscura* + *243. T. leptosoma* + *244. T. tanggulaensis\** +

*245. T. xiangxiensis\** + *246. T. xiqiensis\** + *247. T. daqiaoensis\** + *248. T. brevibarba\** + *249. T. crassilabris\** + *250. T. yaopeizhii* + *251. Nemacheilus obscurus* + *252. Paracobitis variegates* + + *253. P. potanini\** + + *254. P. wujiangensis\** + *255. Oreias dabryi* + + *256. Sphaerophysa dianchiensis\** + *257. Yunnanilus nigromaculatus\** + *258. Y. pleurotaenia\** + *259. Y. caohaiensis\** + *260. Y. sichuanensis\** + *261. Y. longibulla\** + *262. Schistura dabryi* +

*264. S. fasciolata* + *265. S. incerta* + *266. S. xiangxiensis\** + *267. Botia superciliaris* + + *268. B. reevesae\** +

*269. Parabotia fasciata* + + + *270. P. bimaculata\** + + + + *271. P. maculosa* + + + *272. P. kiangsiensis\** + *273. P. banarescui\** + *274. Leptobotia elongata\** VU + + + *275. L. taeniops\** + +

Threat status

Riverhead

Upper reach Middle reach

Lower reach Estuary


*203. C. (C.) carpio* + + + + *204. Carassius auratus auratus* + + + +

*205. Vanmanenia stenosoma* + + *206. V. pinchowensis* + *207. V. tetraloba* + *208. Pseudogastromyzon fangi* + *209. Paraprotomyzon multifasciatus* +

*211. P. lungkowensis\** + + *212. Beaufortia szechuanensis\** +

*214. B. liui\** + *215. Lepturichthys fimbriata\** + + *216. Hemimyzon yaotanensis\** VU + *217. Jinshaia abbreviata\** + *218. J. sinensis\** + *219. Sinogastromyzon hsiashiensis\** + *220. S. sichuangensis\** + + *221. S. szechuanensis\** + + *222. Metahomaloptera omeiensis omeiensis\** + + *223. M. o. hangshuiensis\** +

*224. Triplophysa markehenensis\** + + *225. T. stewarti* + *226. T. orientalis* +

*227. T. bleekeri\** + +

*182. S. (R.) parvus\** EW + *183. S. (R.) ninglangensis\** EN + *184. S. (R.) microstomus\** EN + *185. S. (R.) labrosa\** EN + *186. S. (R.) longibarbus\** CR + *187. S. (R.) davidi\** + + *188. Ptychobarbus kaznakovi* VU + + *189. P.chungtienensis gezaensis\** + *190. P. c. chungtienensis\** EN + *191. Gymnodiptychus pachycheilus* EN + *192. G. potanini potanini\** + *193. G. p. firmispinatus\** + *194. Schizopygopsis malacanthus malacanthus\** + + *195. S. m. chengi\** + *196. S. kialingensis\** + *197. S. malacanthus baooxingensis\** + *198. Herzensteinia microcephalus\** + + *199. Procypris rabaudi\** VU + + *200. Cyprinus (Mesocyprinus) micristius\** EN + *201. C. (Cyprinus) chilia* + *202. C. (C.) qionghaiensis\** EN +

**Homalopteridae**

**Cobitidae**

*210. P. niulanjiangensis\** 

*213. B. niulanensis\** 

Threat status

Riverhead Upper reach Middle reach

Lower reach Estuary

**Order Family**  *Species*


**Order Family**  *Species*

**Clariidae**

**VI. Osmeriformes Salangidae** 

**VII. Salmoniformes Salmonidae** 

**Atherinidae** 

**X. Beloniformes** 

**Poeciliidae**

**Synbranchidae**

**XI. Cypriodontiformes Oryziatidae** 

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 61

*319. Glyptothorax fukiensis fukiensis* + + + *320. G. sinense sinense\** + + *321. Euchiloglanis kishinouyei\** CR + + *322. E. davidi\** EN + *323. Pareuchiloglanis sinensis\** EN + + *324. P. feae* + *325. P. sichuanensis\** + *326. P. robusta\** + *327. P. anteanalis\** +

*328. Clarias fuscus* + + +

*337. Hucho bleekeri\** EN + +

**Hemiramphidae** + +

*347. O. latipes sinensis* VU +

*348. Gambusia affinis* + +

*336. Plecoglossus altivelis* VU

**VIII. Mugiliformes Mugilidae**

**IX. Atheriniformes**

**XII. Synbranchiformes**

**XIII. Scorpaeniformes**

*329. Protosalanx chinensis* + + + *330. Hemisalanx brachyrostralis\** + + + *331. H. prognathus* + + *332. Salanx ariakensis* + *333. Neosalanx oligodontis* + + + *334. N. taihuensis* + + + + *335. N. andersoni* +

*338. Brachymystax lenok* VU + + +

*339. Liza carinatus* + *340. L. haematocheila* + *341. Mugil cephalus* + + *342. Osteomugil ophuyseni* +

*343. Allanetta bleekeri* + +

*345. Hyporhamphus intermedius* + + + + *345. H. sajori* +

*346. Oryzias latipes* + + + +

*349. Monopterus albus* + + + +

Threat status

Riverhead

Upper reach Middle reach

Lower reach Estuary


*283. Cobitis sinensis* + + + + *284. C. taenia* + + *285. C. rarus* + *286. C. macrostigma\** + + *287. Misgurnus anguillicaudatus* + + + + *288. Paramisgurnus dabrynus* + + + +

*289. Pelteobagrus fulvidraco* + + + + *290. P. eupogon\** VU + + + + *291. P. vachelli* + + + + *292. P. nitidus* + + + *293. Leiocassis longirostris* + + + + *294. L. crassilabris* + + +

*297. Pseudobagrus ussuriensis* + + + + *298. P. pratti\** + + + *299. P. truncatus* + + + + *300. P. ondon* + + *301. P. taeniatus* + + +

*304. P. tenuis* + + +

*310. Silurus asotus* + + + + *311. S. meridionalis* + + +

*276. L. pellegrini* + *277. L. guilinensis* + *278. L. microphthalma\** + *279. L. tchangi\** + *280. L. tientaiensis hansuiensis\** + *281. L. rubrilabris\** + + *282. L. orientalis* +

**V. Siluriformes Bagridae**

**Siluridae**

**Amblycipitidae**

**Sisoridae**

*295. L. longibarbus\** CR + *296. L. tenuifurcatus* + +

*302. P. analis\** + *303. P. medianalis\** EN +

*305. P. emarginatus* + + *306. P. brevicaudatus\** + + *307. P. omeihensis\** +

*312. S. mento\** EN +

*313. Liobagrus marginatus\** + + *314. L. anguillicauda* + *315. L. kingi\** EN +

*308. P. adiposalis* + + *309. Mystus macropterus* + + +

*316. L. nigricauda\** + + *317. L. styani\** + + *318. L. marginatoides\** + +

Threat status

Riverhead Upper reach Middle reach

Lower reach Estuary

**Order Family**  *Species*


**Order Family**  *Species*

**XV. Pleuronectiformes Cynoglossidae**

**XVI. Tetrodontiformes** 

Endangered; VU: Vulnerable; +: Present

Wuhan, China.

**7. References** 

**Tetrodontidae**

Appendix 1. List and distribution of fishes in the Yangtze River basin

the Yangtze River. Science Press, Beijing, China.

Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 63

*387. Lophiogobius ocellicauda* + *388. Odontamblyopus rubicundus* + + *389. Synechogobius ommaturus* + *390. Tridentiger trigonocephalus* + + *391. T. barbatus* + *392. Cryptocentrus filifer* + *393. Luciogobius guttatus* + *394. Amblychaeturichthys hexanema* + *395. Taeniodides cirratus* + *396. Oxuderces dentatus* + *397. Trypauchen vagina* + *398. Periophthalmus cantonensis* + *399. Boleophthalmus pectinirostris* + *400. Scartelaos histiophorus* +

*401. Cynoglossus (Areliscus) semilaevis* + *402. C. (A.) abbreviatus* + *403. C. (A.) gracilis* + + *404. C. (Cynoglossoides) robustus* +

*405. Takifugu obscurus* + + + *406. T. coronoidus\** EN + + *407. T. flavidus* EN + *408. T. ocellatus* + *409. T. vermicularis* + *410. T. xanthopterus* + *411. T. pseudommus* + *412. T. alboplumbeus* + *413. T. bimaculatus* + *414. T. porphyreus* + *415. T. reticularis* + *416. T. niphobles* + \*: Endemic fish species; EX: Extinct; EW: Extinct in the wild; CR: Critically endangered; EN:

Anonymous, Department of Ichthyology, Institute of Hydrobiology, CAS (1976). Fishes of

Anonymous (1980). The fishes of Hunan Province. Hunan Science & Technology Press,

Cao, W. (1992). Freshwater fish resources of China. In: Cultivation of the Chinese freshwater

fishes. Liu, J. & He, B. (Eds). 30-64, Science Press, Beijing, China.

Threat status

Riverhead

Upper reach Middle reach

Lower reach Estuary



\*: Endemic fish species; EX: Extinct; EW: Extinct in the wild; CR: Critically endangered; EN: Endangered; VU: Vulnerable; +: Present

Appendix 1. List and distribution of fishes in the Yangtze River basin

#### **7. References**

62 Ecosystems Biodiversity

*350. Trachidermus fasciatus* EN + +

*351. Lateolabrax maculatus* +

*353. S. chuatsi* + + + + *354. S. knerii* + + + *355. S. scherzeri* + + + + *356. S. undulats* VU + + *357. Coreosiniperca roulei* VU + + *358. Coreoperca obscura* +

*359. Macropodus chinensis* + + + + *360. M. opercularis* + + +

*361. Channa argus* + + + + *362. C. asiatica* + + + *363. C. maculata* +

*367. Eleutheronema tetradactylum* +

*368. Terapon jarbua* +

*369. Repomucenus olidus* +

*370. Hypseleotris swinhonis* + + + + *371. Odontobutis obscura* + + + *372. Bostrichthys sinensis* + *373. Eleotris oxycephala* + *374. Prionobutis koilomatodon* +

*375. Mugilogobius myxodermus* + + + + *376. M. polylepis\** EN + + *377. Ctenogobius giurinus* + + + + *378. C. multimaculatus* + *379. Ctenogobius shennongensis\** EN +

*380. Acanthogobius elongata* + *381. Chaeturichthys stigmatias* + *382. Ctenogobius brunneus* + + +

*384. C. cliffordpopei* + + + +

*386. Glossogobius giuris* +

*383. C. szechuanensis\** EN +

*385. C. chengtuensis\** +

*364. Sinobdella sinensis* + + *365. Mastacembelus aculeatus* + + + *366. M. armatus* + + +

*352. Siniperca whiteheadi* +

Threat status

Riverhead Upper reach Middle reach

Lower reach Estuary

**Order Family**  *Species*

**Cottidae** 

**Belontiidae** 

**Mastacembelidae** 

**Polynemidae** 

**Callionymidae** 

**Eleotridae** 

**Gobiidae**

**XIV. Perciformes Serranidae**

**Channidae**

**Terapontidae**

Anonymous, Department of Ichthyology, Institute of Hydrobiology, CAS (1976). Fishes of the Yangtze River. Science Press, Beijing, China.


Distribution, Endemism and Conservation Status of Fishes in the Yangtze River Basin, China 65

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**4** 

**Biodiversity and Conservation of the** 

Patricia Miloslavich1, Alberto Martín1, Eduardo Klein1, Yusbelly Díaz1, Carlos A. Lasso2, Juan José Cárdenas3 and Oscar M. Lasso-Alcalá4 *1Universidad Simón Bolívar, Departamento de Estudios Ambientales, Caracas* 

The Orinoco is one of the largest rivers in South America (2,150 Km). Globally, it is the third in water flow (yearly average of 39,000m3/s), and the fifth in sediment transportation (150 million tons/year). The Orinoco basin extends for nearly a million square kilometers within Colombian and Venezuelan territories, and is characterized by at least ten large terrestrial and aquatic eco-regions including its opening into the Atlantic through the vast Orinoco Delta (located between 07° 46´ to 10° 00´ N, and 59° 50´ to 62° 35´ W) (Michelangeli, 2000; Bone et al., 2004; Lasso et al., 2010). These deltaic plains were formed by the combined action of sediment and freshwater discharges from the Orinoco, with the tides on a flat alluvial plain (Miloslavich et al., 2011) creating a dynamic ecosystem of fluvial and estuarine habitats. The boundaries between these two habitats are defined according to their altitude above sea level and tidal influence (Lasso & Sánchez-Duarte, 2011), with the fluvial delta corresponding to the mid and high delta according to Cervigón (1985). The lower limit of the fluvial delta varies due to seasonal annual fluctuations in freshwater discharge from the Orinoco, related to regional and, even local, precipitation regimes, and a salt wedge from the sea that moves inward with the incoming tide. In the estuarine delta, the ecological boundary of the fluvial delta is the limit at which the sea water influences the main stream and its channels, while the ecological boundary with the sea is a fringe, which is variable in size and forms after sand or mud bars at the opening of the seaward channels. Along this longitudinal zone from the upper to the lower delta, a geomorphological, physico-chemical, and therefore, biological gradient can be observed. In addition to this longitudinal gradient, a very important transversal gradient also exists, that creates particular lentic ecosystems with specialized biota. Within the Atlantic, the major areas of influence of the Orinoco are (1) the Gulf of Paria, a semi-enclosed area between the Araya Peninsula (Venezuela) and the

**1.1 Oceanographic features and eco-regions of the Orinoco Delta** 

**1. Introduction** 

 **Estuarine and Marine Ecosystems** 

 **of the Venezuelan Orinoco Delta** 

*2Instituto Alexander von Humboldt, Bogotá* 

*4Fundación La Salle de Ciencias Naturales, Museo de Historia Natural La Salle, Caracas* 

*3Fundatún, Caracas* 

*1,3,4Venezuela 2Colombia* 

productivity and improvement of ecological environment in Lake Honghu. Honghu Research Group, Institute of Hydrobiology, CAS (Ed). 162-171, China Ocean Press, Beijing, China.

