Tài liệu Báo cáo Nghiên cứu khoa học Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp: Fish breeding practices and stock improvement strategies in
Vietnam in relation to common carp
Christopher M Austin
Pham Anh Tuan
Thai Thanh Binh
Le Quang Hung
Nguyen Thi Tan
School of Science and Primary Industries
Faculty of Health, Education and Science
Charles Darwin University, Casuarina Campus, Darwin, Northern Territory 0909,
Australia
Research Institute for Aquaculture No I
(Ministry of Fisheries)
Dinh Bang, Tu Son, Bac Ninh
Vietnam
June 2007
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
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Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
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CONTENTS
List of Figures..................................................................................................................4
List of Tables ..............
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Fish breeding practices and stock improvement strategies in
Vietnam in relation to common carp
Christopher M Austin
Pham Anh Tuan
Thai Thanh Binh
Le Quang Hung
Nguyen Thi Tan
School of Science and Primary Industries
Faculty of Health, Education and Science
Charles Darwin University, Casuarina Campus, Darwin, Northern Territory 0909,
Australia
Research Institute for Aquaculture No I
(Ministry of Fisheries)
Dinh Bang, Tu Son, Bac Ninh
Vietnam
June 2007
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
___________________________________________________________________________
___________________________________________________________________________
Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
2
CONTENTS
List of Figures..................................................................................................................4
List of Tables ...................................................................................................................6
Summary..........................................................................................................................8
1. Introduction...............................................................................................................11
1.1 Taxonomy and distribution................................................................................11
1.2 Biology of common carp .....................................................................................13
1.3 Common carp culture .........................................................................................14
2. Common carp culture in Vietnam...........................................................................17
2.1 Summary of socio-economic survey of common carp culture in Vietnam ....19
2.1.1 Carp farmer family profile .............................................................................21
2.1.2 Common carp culture.....................................................................................21
2.1.3 Suggestion of fish farmers .............................................................................27
3. Common carp breeding programs in Vietnam. .....................................................28
3.1 Introduction.........................................................................................................28
3.2 Crossbreeding of common carp .........................................................................29
3.3 Mass selection of common carp .........................................................................31
3.4 Family selection of common carp ......................................................................37
3.5 Combination of family and individual selection of common carp..................38
4. Overview molecular genetic studies on common carp in the world .....................42
5. Genetic diversity of common carp in Vietnam using direct sequencing and SSCP
analysis of the DNA control region..................................................................45
5.1 Objective ..............................................................................................................47
5.2 Materials and Methods .......................................................................................47
5.2.1 Sample collection...........................................................................................47
5.2.2 DNA extraction and sequencing of control region ........................................49
5.2.3 Single Strand Conformation Polymorphism (SSCP) amplification...............50
5.2.4 Data analysis ..................................................................................................51
5.3 Results ..................................................................................................................52
5.3.1 Control region sequences and SSCP variation...............................................52
5.3.2 Genetic differentiation and relationships among populations........................54
5.4 Discussion.............................................................................................................59
5.4.1 Control region sequence variation and utility of the SSCP techniques .........59
5.4.2 Genetic diversity of common carp in Vietnam ..............................................60
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
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5.4.3 Insights into the dissemination of cultured common carp in Vietnam ..........63
5.4.4 Conservation of wild carp stocks ...................................................................65
5.4.5 Conclusion .....................................................................................................68
6. Genetic diversity of common carp in Vietnam using four microsatellite loci .....69
6.1 Objectives.............................................................................................................72
6.2 Materials and Methods .......................................................................................72
6.2.1 Sample collection and DNA extraction..........................................................72
6.2.2 Data collection ...............................................................................................72
6.2.3 Genetic diversity analysis ..............................................................................73
6.2.4 Genetic differentiation between populations .................................................74
6.3 Results ..................................................................................................................75
6.3.1 Within population variation ...........................................................................75
6.3.2 Genetic differentiation and relationships among populations........................79
6.4 Discussion.............................................................................................................85
6.4.1 Genetic diversity within common carp populations.......................................85
6.4.2 Differentiation between populations ..............................................................88
6.4.3 Comparison of microsatellite and mitochondrial DNA data..........................90
7. Expanded genetic analysis of common carp stocks from private hatcheries,
farmer ponds and market places .....................................................................93
7.1 Introduction.........................................................................................................93
7.2 Materials and Methods .......................................................................................94
7.2.1 Sample collection and data set .......................................................................94
7.2.2 DNA extraction and Single Strand Conformation Polymorphism (SSCP)
amplification ...........................................................................................................95
7.2.3 Data analysis ..................................................................................................95
7.3 Results ..................................................................................................................96
7.3.1 SSCP variation ...............................................................................................96
7.4 Discussion...........................................................................................................104
7.4.1 Additional insights into diversity of common carp in Vietnam...................104
Appendix ......................................................................................................................108
Reference......................................................................................................................112
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List of Figures
Figure 1.1. Distribution of common carp in the world (FAO 2003)...............................12
Figure 1.2. World production of common carp (FAO 2003)..........................................15
Figure 2.1. Varieties of common cap in Vietnam (A: Bang Giang River, B&F:Dak Lak,
C: Son River red, D: Bac Kan) ...........................................................................18
Figure 2.2. Types of common carp culture in Vietnam (A: Pond culture, B: Rice-fish
culture, C: Integrated aquaculture)......................................................................19
Figure 2.3. The locations at which stakeholders were interviewed for the socio-
economic survey..................................................................................................20
Figure 2.4. Type of common carp culture in Vietnam....................................................22
Figure 2.5. Percent fish species stocked into household ponds in Vietnam ...................23
Figure 2.6. Water source used for common carp culture ................................................23
Figure 2.7. Common carp sources in the farms in Vietnam............................................24
Figure 2.8. Farmer evaluation quality of seed.................................................................26
Figure 2.9. Demand for common carp in Vietnam .........................................................26
Figure 3.1. Mass selection of three blood common carp (Thien and Thang, 1992) .......33
Figure 5.1. Collection localities for Cyprinus carpio L. samples in Vietnam.................49
Figure 5.2. Silver stained polyacrylamide gel showing the eight SSCP variants detected
in common carp populations in Vietnam (a). Neighbour-joining tree
reconstruction derived from CR sequences, using HKY+I+G model of evolution.
Bootstrap values are based on 1,000 replicates. Bootstrap value is given for
nodes with at least 50% or more support (b).......................................................66
Figure 5.3. Relationships among common carp from wild and hatchery population in
Vietnam using the unbiased genetic distance of Roger (1972) and UPGMA
joining method. A, B, and C are SSCP haplotypes which predominate in each
cluster. .................................................................................................................67
Figure 5.4. MDS plot of pairwise Fst value among hatchery and wild populations of
common carp in Vietnam. Population codes are given in Table 5.1...................68
Figure 6.1.Allele number and distribution of allele frequencies for Hungarian,
Indonesian and Vietnamese experiemtal common carp populations at each
microsatellite locus. ............................................................................................80
Figure 6.2. UPGMA dendrogram of common carp populations in Vietnam based on
matrixes of genetic distance (Nei et al., 1983)....................................................84
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
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Figure 6.3. MDS plot of paiwise Fst value among experimental, hatchery and wild
populations of common carp in Vietnam, (a) based on microsatellite data, (b)
mitochondrial DNA data. Population codes are given in Table 5.1. ..................86
Figure 7.1. Collection localities for Cyprinus carpio L. samples in Vietnam. Population
code are given in Table 7.1. ................................................................................98
Figure 7.2. Haplotype diversity of Common carp groups in Vietnam base on SSCP
analyses. ............................................................................................................101
Figure 7.3. Relationships among common carp from experimental, provincial hatchery,
private hatchery, private pond, market, wild populations in Vietnam using the
unbiased genetic distance of Rogers (1972) and UPGMA joining methods. A, B,
C are SSCP haplotypes which predominate in each cluster. Population codes are
given in Table 7.1..............................................................................................102
Figure 7.4. Multidimension scaling (MDS) plot of pairwise Fst values among common
carp from experimental, provincial hatchery, private hatchery, private pond,
market, wild populations in Vietnam. Population codes are given in Table 7.1. A,
B, C are main groups.........................................................................................103
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
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Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
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List of Tables
Table 2.1. Number of fish farms surveyed......................................................................21
Table 2.2. Frequency changed common carp broodstocks in hatcheries are changed....25
Table 3.1. Survival rate (%) for fry and fingerling of Vietnamese common carp (V),
Hungarian common carp and their reciprocal hybrids (VH, HV) (Thien and
Thang, 1992) .......................................................................................................30
Table 3.2 Morphology and morphometrics of common carp varieties and their hybrids
(H: Hungarian; Y: Indonesian Yellow; V: Vietnamese White) (Nguyen et al.,
2005) ...................................................................................................................31
Table 3.3. Adjusted average body weight of the common carp in an experiment on
determination of realized heritability in 1988 (Thien and Thang, 1992)............32
Table 3.4. Summary data of the mass individual selection of the hybrid stocks of
common carp (V: Vietnamese, H: Hungarian and Y: Indonesian yellow common
carp) (Tran and Nguyen, 1992)...........................................................................34
Table 3.5. Heritability (h2) of the body weight of hybrid common carp Hungarian x
(Vietnamese x Yellow) (Tran and Nguyen, 1992)..............................................35
Table 3.6. Growth rate of common carp of the F3 and F5 selected generations in a grow-
out pond; Stocks [Hungarian x (Vietnamese x Yellow)] in Communal stocking
in 1995 (Nguyen, 2005). .....................................................................................36
Table 3.7. Body weight of common carp in pure stocks and their hybrids reared in the
same pond, 1995 (Thien and Thang, 1992). .......................................................37
Table 3.8. Current crossbreeding between carp lines to produce 86 families (Nguyen,
2005) ...................................................................................................................40
Table 5.1. Location, code and number of samples sequenced and analysed by the SSCP
technique. ............................................................................................................48
Table 5.2. Number of haplotypes and haplotype diversity in each common carp
population. Population code given in Table 5.1..................................................57
Table 5.3. Pair-wise estimate of variance of haplotype frequencies (Fst) among of
samples. Population codes given in Table 5.1. ...................................................58
Table 5.4. AMOVA results for three groups (experimental, hatchery, wild) of 20
common carp populations base on SSCP data. (Intra = intrapopulation, Inter =
interpopulation, values are %).............................................................................59
Table 6.1. Characteristics of Cyprinus carpio microsatellite loci tested.........................73
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Table 6.2. Genetic variability of four microsatellite loci in 20 populations for common
carp in Vietnam. Population codes given in Table 5.1. ......................................77
Table 6.3. Number of private alleles at four microsatellite loci in 20 common carp
populations and group. The population codes are given in Table 5.1.................78
Table 6.4. Pairwise Fst values between 20 common carp populations in Vietnam based
on four microsatellite loci. Population codes given Table 5.1............................81
Table 6.5.Results of assignment test (self-classification) of common carp individuals
based on four microsatellite loci. Population code are given in Table 5.1. ........82
Table 6.6. Genetic diversity of experimental, hatchery and wild common carp groups in
Vietnam based on variation at four microsatellite loci (Intra = intrapopulation,
Inter = interpopulation, values are %).................................................................85
Table 7.1. Location, code and number of common carp sample fro Vietnam analysed by
the SSCP technique.............................................................................................97
Table 7.2. Number of haplotype (N) and haplotype diversity (Hd) in each common carp
population in Vietnam.........................................................................................99
Table 7.3. Number of population (N), haplotype (n) and haplotype diversity (Hd) of six
common carp groups in Vietnam. .....................................................................100
Table 7.4. AMOVA results for six groups (experimental, provincial hatchery, private
hatchery, private pond, market and wild) of common carp population in Vietnam
base on SSCP data. (N = number of population was analysed, Intra =
intrapopulation, Inter = interpopulation, value are %)......................................104
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
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Summary
This document brings together, for the first time, information from diverse sources
relating to common carp breeding and genetic improvement strategies in Vietnam.
These sources include the results of a survey of common carp farmers and hatchery
operators, published and unpublished reports in Vietnamese on fish breeding and
genetic improvement programs and experiments and the results of a comprehensive
molecular genetic analysis of common carp stocks throughout Vietnam.
The survey of common carp farmers and hatchery operators was conducted through
interviews using standardised questionnaires and workshop. These activities confirmed
common carp as the principal species for freshwater aquaculture in north Vietnam and
that farmers were well informed about the significance of making use of genetically
improved carp to improve productivity. The responses to the survey indicated that the
majority of farmers believed they were utilising government produced genetically
improved carp strains. Farmers emphasised difficulties in acquiring general knowledge
and new skills associated with carp breeding and indicated they would welcome greater
opportunities for training and participating in workshops. A key outcome of the survey
was that while farmers were aware of the importance of using genetically improved
strains they had difficulty in accessing such stocks in sufficient quantities to make an
impact on the gene pool of their farmed stocks. The key information in this regard is
that farmers were only accessing new genetically improved stocks on from a 1-4 year
cycle and even when introducing new stocks these would only make a 10% contribution
to farm's or hatchery's existing broodstock. This, coupled with the fact that farmers and
hatchery operators spawn their fish in communal ponds where there is no control over
matings means that new broodstock may make only minimal contributions to the
production of fry and fingerlings. This problem could be circumvented if farmers had
the skills and equipment to undertake controlled and induced spawning of carp
broodstock using the techniques of gamete stripping and artificial fertilisation.
A survey of the Vietnamese literature on the genetic improvement of carp for pond
aquaculture production indicates that a large scale and ongoing selective breeding and
broodstock development and management programme has been in place for over 30
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years supported by the Vietnamese government. This program has included a survey of
indigenous Vietnamese carp genetic resources, the importation of carp strains from
Indonesia and Europe, selective breeding trials and genetic improvement programmes
involving cross breeding and mass and family selection. Growth and heritability data
collected as part of these programmes support a significant increase in the productivity
of the genetically improved carp strains. However these trials have been undertaken
exclusively in well managed research ponds. Thus an important requirement is the
conduct of trials of the relative performance of different carp strains within farmer’s
ponds as these present very different biological, physical and management
environments to those in research ponds. Further, while the Vietnamese government
genetic improvement program was implemented to improve the livelihoods of carp
farmers there does not seem to have been a concerted program to widely disseminate
genetically improved carp to farmers.
The application of modern molecular genetics to an analysis of genetic diversity within
and between Vietnamese carp stocks provides very important and novel insights into the
management and dissemination of carp stocks through out Vietnamese. An important
preliminary finding was that the three main experimental lines or strains of common
carp could be readily distinguished from each other and that all three experimental lines
had reduced variability. This means that the patterns of genetic variability within
populations and the relationships between populations provide information on the
mixing and origin of stocks. The overall, conclusions from the genetic analysis is that
the dissemination of genetically improved carp strains has only been a partial success.
While a number of common carp stocks from provincial government hatcheries had
elevated diversity levels and represented mixtures of Indonesian and Vietnamese carp
most hatcheries appear to be largely or completely derived from Vietnamese carp stocks
and some of these had very low levels of diversity indicating inbreeding and poor
broodstock management. Surprisingly, there was very little evidence that introduced
Hungarian carp had contributed to gene pools in hatcheries or in the market place given
the strongly held believe of that this strain has positive characteristics especially in
relation to growth and is thought to has been widely dissemination. However, the
genetic data are consistent with pond trials which indicated this strain has poorer
survival compared to the other stains. In fact, the genetic profiles of all the carp sampled
from the markets was consistent with their derivation from Vietnamese stocks and that
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small scale farmers may not be benefiting from the significant investment in the
development of genetically improved common carp.
There are three important recommendations from a synthesis of the information from
the farmer survey, the Vietnamese carp breeding program and the genetic data. Firstly,
there is the need for the provision of a greater level of technical training and workshops
for farmers specifically relating to carp breeding and broodstock management. Secondly,
more effective strategies are needed to be developed for the dissemination of genetically
improved broodstock to ensure the benefits of better performing stocks are made
available, especially to small scale farmers. Thirdly, on-farm trials need to be
conducted to evaluate the performance of different breeds and strains of common carp
under different grow-out conditions and at a range of locations. This last
recommendation would have the added benefit of encouraging the participation of small
scale farmers in the research and the evaluation process of different strains.
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1. Introduction
1.1 Taxonomy and distribution
Common carp (Cyprinus carpio L.) occur in water ways throughout Eurasia, from
Western Europe through to China, Korea, Japan and South East Asia and from Siberia,
south of latitude 600 N, to the Mediterranean and India (Kohlmann and Kersten, 1999).
The actual origin and natural distribution of common carp is disputed by some authors
due to its long history of domestication in both Europe and Asia which have led to
many translocations over a significant period of time (Balon, 1995). Because of the long
documented cultivation history of common carp in China, some scientists considered
that the ancestor of European domestic carp were derived from Asian common carp
stocks, during ancient Greek and Roman periods (Chiba et al., 1966; Vooren, 1972).
Others consider that the common carp is indigenous to Europe and in fact postulate a
European origin for wild carp and subsequent dispersal east to Siberia and China (Balon,
1995; Kottelat, 1997).
Due to its popularity as an aquaculture and ornamental species, common carp has been
widely translocated, outside its European and Asian distribution. As a result of these
transfers and introductions, it is now perhaps the most widespread species of freshwater
fish in the world, with naturally reproducing populations established in many countries
in both northern and southern hemispheres. FAO (1998) lists introductions of common
carp into 124 countries, of which 81 are recorded as having established feral populations
or viable aquaculture stocks.
Cyprinus carpio is taxonomically a most confusing species with over 30 synonyms
listed on FishBase ( Based on just recent
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taxonomic treatments, opinions vary widely: Balon (2004) and Kirpitchnikov (1999)
recognised three subspecies: European common carp (Cyprinus carpio carpio Linnaeus,
1758), and Far Eastern common carp (C. carpio haematopterus Temminck & Schlegel,
1845), South East Asian common carp (C. carpio viridiviolaceus Lacepede, 1803),
whereas Kottelat (2001) recognised European common carp as Cyprinus carpio
Linnaeus, 1758 and Asian common carp Cyprinus rubrofuscus Lacepede, 1803. These
taxa are distinguished mainly by morphology, such as number of gill rakers and scales,
shape and color characteristics. However, there is often overlap in these traits which
may be in part due to stock mixing and hybridization which may have blurred
taxonomic boundaries. Moreover, the domestication of common carp has not only led to
changes in body proportion, scalation and colour, but also in physiological
characteristics (Balon, 1995; Baruš et al., 2002).
Figure 1.1. Distribution of common carp in the world (FAO 2003)
The taxonomic uncertainties, compounded by translocations, and the development of
phenotypically distinctive domesticated lines, invites the use of molecular markers to
elucidate the taxonomy of common carp and genetic relationships among stocks (Balon,
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1995; Lever, 1996). There is also a clear need to examine the status of possible wild
common carp gene pools to determine if there is a need to conserve genetic resources in
this species. Lever (1996) considered that the wild ancestor of the common carp may be
a single species, Cyprinus carpio, widely distributed from the Danube to Amur Rivers.
While the existence of several self-sustaining wild populations of carp have been
documented (Kohlmann and Kersten, 1999; Paaver and Tammert, 1993), Komen (1990)
believes that truly self-sustaining wild populations of common carp are probably rare.
1.2 Biology of common carp
Common carp is a largely benthic species that prefers shallow water habitats covered
with aquatic weeds and grasses. It is an omnivorous fish that mostly feeds on the bottom
but can exploit all levels in the water column. The natural diet of carp is dominated by
chironomids, snails, young clams, shrimps and other benthic animals. This species also
consumes aquatic plants, filamentous algae, seeds of plants and organic detritus. Under
pond culture conditions, common carp will take soybean and peanut cakes, rice and
wheat bran (Zhong, 1989).
The common carp may be sexually mature as early as the end of its first year; however
it typically requires three to four years to reach this stage (Cooper, 1987). According to
Linhart et al. (1995) common carp have a high fecundity for a freshwater species
producing 100,000 to 300,000 eggs per kg body weight with reports of as many as
360,000 to 599,000 eggs per female. The eggs are sticky in nature, and attach to aquatic
weed and other material after spawning.
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Common carp reach 0.6 to 1.0 kg body weight within one season in the polyculture fish
ponds of subtropical/tropical areas (FAO, 2004). Currently the world record for the
largest carp stands at 34.3 kg. In their natural range carp can live up to 15 years,
however they have been reported in some areas living to over 24 years of age with
males often living longer than females (Balon, 1995).
1.3 Common carp culture
Common carp is the most extensively cultivated freshwater fish species in the world
(Chiba et al., 1966; Komen, 1990; Wohlfarth, 1984; Zhou et al., 2004b). This fish has
several advantages that make it popular for commercial culture: (1) very fast growth
rate, (2) high environment tolerance, (3) ease of handling, (4) ability to be raised in high
density, (5) ability to utilise artificial diet with relatively low protein content, and (6)
occurrence of highly productive strains and breeds produced from long-term
domestication and selective breeding (Kirpitchnikov, 1999).
Culturing and breeding of common carp has a long history dating back about 4,000
years in China and close to 2,000 years in Europe. Several special breeding centres have
been developed in different regions of Europe, like the Czech Republic, Germany and
Hungary, as well as Russia and Ukraine. China and Japan are the ancient culturing
centers in Asia, but during the last decades India, Indonesia and Vietnam have started to
culture common carp as a result of deliberate fish importation and acclimatization
activities (Bakos and Gorda, 2001).
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Annual production of common carp worldwide is over three million metric tons (FAO,
2003) (Fig 1.2). In Asian countries, common carp contributed 17% to total carp
production from aquaculture in 2001 (Gupta et al., 2005).
Figure 1.2. World production of common carp (FAO 2003).
Li (2001) reported that production of common carp reached 2.05 million tons in 1999
and accounted for 20% of total freshwater fish output in China. In Indonesia, common
carp production reached 178,362 tons in 1996, and accounts for 54.3% of total cultured
freshwater fish in this country (Hardjamulia et al., 2001). In Europe, common carp is by
far the most important freshwater fish with annual aquaculture yield of about 220,000
tons, which is higher than the European yield of rainbow trout (Linhart et al., 2002).
Breeding and culture of common carp has been the backbone of fish farming in many
European countries. For example, in 2001 common carp production reached 14,000,
10,500, 17,000 and 21,000 tons in Hungary, Germany, Czech, and Poland respectively.
Common carp are cultured in a wide range of environments including ponds, cages,
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tanks, reservoirs and rice-fields, as monoculture and polyculture with a variety of other
species (FAO, 2001).
In addition to production for food, common carp have been selectively bred for a variety
of colors and color patterns for the ornamental fish market (Balon, 1995). Best known
varieties are Koi carps which are called “swimming flowers” and are among the most
expensive of ornamental fish species. Amano (1968) recorded an annual production of
some 10 million fish amounting 1,000,000,000 yen in Japan. Although originally
developed in Japan, Koi carps are now cultured in many parts of the world, including
China, Europe and America (Balon, 1995).
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2. Common carp culture in Vietnam
Common carp (Cyprinus carpio L.) is thought to be indigenous to northern Vietnam,
and translocated to southern Vietnam (Nguyen and Ngo, 2001). Eight local varieties
have been recognised in Vietnam: white carp, Bac Kan carp, high body carp, Ho Tay
carp, South Hai Van carp, red carp, violet carp, and reduced scale carp. These varieties
differ in morphology, colour, distribution, and some other biological characteristics
(Tran, 1983). The white carp is one of the most popular and important fish in
aquaculture in Vietnam. In the study by Tran (1983) it was found that indigenous strains
of common carp have poor growth rates and highly variable color and scale phenotypes.
For example, the Bac Kan strain is unusually elongated in shape and is morphologically
distinct from other strains. It commonly attains a weight of only 70-80 g in first year in
polyculture and 160-200 g in the second year when grown in low input rice-field.
Nevertheless, it is an important strain as it is adapted to the rice-field environment and
farmers can maintain broodstock that do not depend on wild seed. The most important
traits of the Bac Kan strain are that it can be cultured in shallow water and is tolerant of
fluctuations of water temperature that characterises this environment. Another useful
trait for culture in terraced rice-field, in which water flows from terraced field to the
next below, is that the fish rarely leave the fields even during flooding when water spills
across dikes (Edwards et al., 2000). The local “rice field” common carp strains are
called “resident fish” or “fix- home fish” because of this useful characteristic (Tran,
1983) (Fig 2.1).
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Figure 2.1. Varieties of common cap in Vietnam (A: Bang Giang River, B&F:Dak Lak,
C: Son River red, D: Bac Kan)
In general, Vietnamese common carp is considered a good aquaculture species because
it exploits natural pond productivity, has good survival rate and the flesh has low fat
content (Bakos and Gorda, 2001). There are however concerns about wild carp stocks
which are thought to be in decline because of excessive harvesting and crossbreeding
with introduced carp stocks (Nguyen and Ngo, 2001).
Common carp have been cultivating in polyculture system in Vietnam including pond
culture with a range other species, rice-fish, cage and integrated aquaculture with
poultry and pig (Fig 2.2).
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
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Figure 2.2. Types of common carp culture in Vietnam (A: Pond culture, B: Rice-fish
culture, C: Integrated aquaculture).
2.1 Summary of socio-economic survey of common carp culture in
Vietnam
Socio-economic data were collected by interviews, using standardised questionnaires,
with farmers, private hatchery owners and provincial hatchery managers from 21
provinces representing a total of 133 interviewees mostly in the highland (Appendix 1,
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Figure 2.3). Data were analysed using SPSS 11. The break down of stakeholders
surveyed is presented in Table 2.1.
Figure 2.3. The locations at which stakeholders were interviewed for the socio-
economic survey.
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Table 2.1. Number of fish farms surveyed
Farm N Percentage (%)
Farmers 91 68.4
Provincial hatchery managers 30 22.6
Private hatchery owners 12 9.0
Total 133 100.0
2.1.1 Carp farmer family profile
The age of the farmers ranged from 38.2 to 50 years old in the 21 provinces surveyed.
Over 55% of farmers are women, and 15% from ethnic backgrounds. Farmers learn to
culture fish by many ways, media (television, newspaper), and farmer training.
However, most farmers mainly learn fish culture techniques from each other, especially
their families. The survey results indicated that over 76% of the farmers had not
received any formal training in common carp culture.
2.1.2 Common carp culture
• Type of culture
Common carp is one of the main aquaculture species in Vietnam and they are cultured
in ponds, rice fields, and cages. The results of the survey indicated that farmers have
been predominately using ponds (79%) and with a much smaller proportion using ponds
with rice-fields (12.8%) or just rice-fields (6.8%) for culturing common carp (Fig 2.4).
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78.95%
6.77%12.78%
1.50%
Rice field
Pond
Pond & rice field
Cage
Figure 2.4. Type of common carp culture in Vietnam
• Common carp in polyculture pond
Most farmers surveyed use polyculture techniques. Common carp are cultivated along
with Chinese carp and Indian carp in both ponds and rice fields. More than 8 different
fish species are stocked with common carp (Cyprinus carpio) including grass carp
(Ctenopharyngodon idellus), silver carp (Hypophthalmichthys molitrix), bighead carp
(Aristicchthys nobilis), rohu (Labeo rohita), mrigal (Cirrhinus cirrhosus), tilapia
(Oreochromis niloticus), black carp (Mylopharyngodon piceus), pirapitinga (Piaractus
brachypomus), other species. Of these species common carp (30.9%) is the dominant
species in polycuture ponds (Fig 2.5).
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9.03%
10.87%
11.24%
2.33%
3.38%0.87%
18.53%
30.88%
9.75%
3.12%
Common carp
Grass carp
Silvel carp
Bighead carp
Rohu
Mrigal
Tilapia
Black carp
Pirapitinga
Other
Figure 2.5. Percent fish species stocked into household ponds in Vietnam
• Pond management
Since approximately 78.9 % of the farmers surveyed had access to irrigation canals,
they were able to exchanged pond water at regular intervals. Only 3.8% of the farmers
rely solely on rainwater for aquaculture and were seriously restricted in their capacity to
exchange water (Fig 2.6). Common carp are generally fed directly with soybean, corn,
cassava or indirectly though pond fertilization.
3.80%
78.90%
17.30%
Irrigation water
Rainwater
River, stream water
Figure 2.6. Water source used for common carp culture
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• Seed sources
Common carp cultured in the farms are derived from many different sources. Over
55.6% of seed stocks were obtained directly from private or provincial hatcheries and
20.4% from retailers who buy from a range of sources including from private and
provincial farmers hatcheries, and possibility also from fishermen who obtain stocks
from the wild.
4.93%
20.43%
4.23%
55.62%
14.79%
River
Hatchery
Retailers
Other
Retailers & hatchey
Figure 2.7. Common carp seed sources in the farms in Vietnam
• Common carp strains
Common carp have been cultured in Vietnam for at least a thousand years. The strains
of common carp that are cultured include indigenous carp from rivers and lakes, and
genetically improved carp. Based on farmer’s claims about 79.2% of cultivated carp in
the farms are three blood carp strains that come from government research institutes and
represent several genetically improved forms of carp. The remaining farmers grow carp
from the wild or from unknown sources. Most farmers produce fingerlings in their
ponds form commercial sale and also use these stocks their own farm ponds. A total of
96.2% of the farmers are selling seed to other smaller scale farms.
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• Hatchery establishment and broodstock management
Most hatcheries have been established since 1984 with common carp being the major
fish for spawning. Carp broodstooks are spawned about 1-3 times per year and are
maintained on a diet of soybean, cassava, bud rice and artificial food. All hatcheries
(96%) induce common carp breeding using tradition methods involving mostly
reproduction in ponds or tanks or rice-fields using broodstock mostly composed of
mixed strains and using fibrous material for egg attachment. Most hatcheries change
broodstock every 1-2 year (Table 2), although hatcheries only change from10 to 20% of
their broodstock at any one time.
Table 2.2. Frequency changed common carp broodstocks in hatcheries are changed
Change (Year) Percentageof hatcheries (%)
1 41.2
2 17.6
3-4 32.4
>4 8.8
Like common carp seed, broodstock in the farms and hatcheries are derived from
different sources. Three blood genetically improved broodstock is most common,
mainly obtained from Research Institute for Aquaculture No 1, Bac Ninh (RIA1)
(73.9%) with 4.3% of broodstock representing the Hungarian strain.
• Quality of seed
Quality of fingerlings depends on quality of broodstocks and breeding techniques. Only
25.5% of farmers reported the quality of seed is good (Fig 9) though 62.4% of farmers
did not have any comment.
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11.30%
25.60%
0.60%
62.50%
Good
Moderate
Not good
No comments
Figure 2.8. Farmer evaluation of quality of seed
• Demand for common carp
Farmers generally consider the demand for common carp is increasing in Vietnam.
About 36.8% of the farmer reported the demand of common carp is increasing (Fig 2.9)
compared to 0.7% who thought the converse. It should be noted that 60.2% had no
comment.
2.26%
60.15%
36.84%
0.75%
Increase
discrease
No comment
No change
Figure 2.9. Demand for common carp in Vietnam
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2.1.3 Suggestion from fish farmers
The suggestions of farmer were collected from 133 interviewees and from 75
participants in two workshop for fish hatchery managers and farmers which were
organised in RIA1 2005 and Thai Nguyen Aquaculture department in 2006. The
suggestions of farmer include:
• Quality of broodstock and seed of common carp should be improved
• Providing good common carp stocks for farmers
• More training fish breeding and cultured techniques for farmers
• Research on reduce common carp seed cost
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3. Common carp breeding programs in Vietnam.
3.1 Introduction
Traditional knowledge supports the existence of there are 8 local varieties of common
carp in Vietnam and the introduction of three exotic strains. The local varieties,
identified on the basic of morphology and coloration are, white scaled, Bac Can, Ho
Tay, South Hai Van, Red, Violet, High Body Depth and Scattered Scale varieties
(Trong, 1983). The introduced common carps are Hungarian scaled, Hungarian mirror
and Indonesian yellow strains.
A government supported common carp selective breeding program has been in place in
Vietnam for over 30 years with the aim of developing and disseminating strains with
high growth and survival rates to fish farmers (Tran and Tran, 1995).
In 1970 and 1975 the mirror and scale strains of Hungarian common carp were
introduced to Vietnam. Indonesian yellow carp was introduced to the south of Vietnam
before 1975 and then transferred to the north in 1978. In the 1970s experiments on
hybridization of Vietnamese white carp with the Hungarian carps were carried out
(Tuong and Thien, 1979; Thien and Tuong, 1983; Thien, 1993). Experiments found
hybrid common carp (F1) to have fast growth and high survival and the best
productivity in farm ponds was obtained from raising hybrid carp. However due to
improper broodstock management, the base stocks of common carp in almost all
hatcheries over the country were gradually losing their diversity, thus decreasing the
effectiveness of breeding programs. Since 1981, research programs have focused on
selection of common carp with the intention of creating a fish breed with stable genetic
qualities. In the first phase (1981-1985) the program focused on the assessment of carp
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stocks for selection. In the second phase (1986-1995) mass selection was carried out
among the hybrid stocks over six generations. Continued family selection was carried
out over two generations in the period of 1996 to 2000, making up the third phase.
3.2 Crossbreeding of common carp
Initially eight varieties of local common carp were investigated, of which white carp, a
variety with high viability is the most popular (Trong 1983). However, this carp and
other varieties of Vietnamese common carp presented slow growth and early maturity.
Attempts aimed at obtaining heterosis by crossing among these varieties were not
successful.
Under Vietnamese conditions, the Hungarian carps showed fast growth and late
maturation but were easily infected with diseases and possessed low viability. The first
hybrid generation (F1) crossing between Vietnamese white carp and Hungarian carp
showed the best characteristics from their parents i.e. high survival rate, fast growth and
attractive appearance. The survival rate of hybrid fry and fingerling was much higher
than that of Hungarian carp (Table 3.1). At the same time survival rate of the hybrids
and Vietnamese carp was similar.
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Table 3.1. Survival rate (%) for fry and fingerling of Vietnamese common carp (V),
Hungarian common carp and their reciprocal hybrids (VH, HV) (Thien and Thang,
1992)
.
Survival rate (%) Stage Crossing
1974 1975 1976
Fry
V
VH
HV
H
51.6
61.6
60.4
22.3
-
70.0
44.3
40.0
71.2
80.0
78.0
37.6
Fingerling
V
VH
HV
H
85.9 ± 9.4
94.9 ± 1.9
81.4 ± 7.5
45.7 ± 5.2
-
76.2 ± 2.9
76.7 ± 2.3
38.6 ± 2.4
78.3 ± 0.2
90.0 ± 3.3
73.0 ± 11.3
46.3 ± 5.1
A more sophisticated cross breeding strategy was subsequently adopted to bring
together a number of positive qualities from different varieties and to improve the
genetic variability of the initial stock for mass selection. At first three hybrid strains
were constructed by crossing Vietnamese carp with Hungarian carp (VH), Vietnamese
carp with yellow carp (VY) and Hungarian carp with yellow carp (HY). Then the males
of each single hybrid were crossed with females of the third strain. The double hybrids
obtained in these crossings have been evaluated and used as stock for further selection
(Fig. 3.1). Assessments of this selection program included comparisons using
morphological, physiological and biochemical characteristics among the above
mentioned pure common carp varieties and their hybrids (Table 3.2).
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Table 3.2 Morphology and morphometrics of common carp varieties and their hybrids
(H: Hungarian; Y: Indonesian Yellow; V: Vietnamese White) (Nguyen et al., 2005)
Descriptions Variaties Hybrids
H Y V HxV HxY VxY
Body weight (g) 24.30 ± 1.41 22.20±1.27 16.30±0.61 21.20±0.91 22.8±1.21 12.90±0.89
Standrd length (cm) 8.20±0.16 3.3±0.18 7.9±0.09 8.1±0.11 8.2±0.15 6.9±0.15
As% of standard length:
Maximal body height 38.1± 0.19 35.1±0.32 30.9±0.25 35.5±0.25 37.3±0.28 32.2±0.30
Minimal body height 14.30±0.13 13.0±0.13 11.9±0.10 14±0.16 13.9±0.17 14.4±0.17
length of head 43.10±0.24 31.90±0.13 31.6±0.16 34.4±0.38 33.1±0.30 32.1±0.40
Dorsal spine to tip most dorsal ray 36.30±0.24 36.6±0.25 33.5±0.16 36.6±0.38 34.4±0.14 37.1±0.30
Intestine length 174.00±1.60 185.7±1.8 145.0±1.3 175±1.4 186±2.20
As% of head length:
Diameter of eye 26.60±0.32 24.0±0.37 29.6±0.49 25.9±0.45 25.4±0.30 27.9±0.50
length of barbell 17.80±0.29 18.6±0.25 18.0±0.21 19.2±0.21 18.2±0.26 17.4±0.30
No. of lateral line scales 37.70±0.20 32.9±0.25 32.0±0.14 32.6±0.12 33.8±0.16 33.4±0.15
No. of Dorsal rays 18.90±0.12 18.3±0.16 20.4±0.16 18.0±0.08 18.2±0.26 19.0±0.15
No. Anal rays 5 5 5 5 5 5
No. of branched stamens in first bow 24.9±0.20 19.7±0.17 7.7±0.18 20.2±0.20 22.7±0.23 20.2±0.18
No. of vertebrae 35.80±0.12 35.10±0.08 34.10±0.08 34.4±0.13 35.00±0.16 34.70±0.20
3.3 Mass selection of common carp
In order to carry out mass individual selection about 5-10 families (one family included
1 female and 3-4 males) of each hybrid stock were bred on the same day. Their eggs
were incubated under the same conditions. The rearing of fry and fingerlings and
culturing them to marketable size were done under similar environmental conditions.
On an average, about 20% of total number marketable fish in each stock were selected
based on the body weight and appearance (big body and small head). The selection
effectiveness was estimated according to Falconer (1960).
R= Sh2 = iδh2
R: effectiveness of selection ; i: intensive of selection
S: selection differential ; δ: average square variation
h2: heritability of the trait (body weight)
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To estimate the coefficient of realized heritability of fish body weight in each selected
generation, the experiments were implemented according to the schema in Figure 3.1.
Before mass selection of marketable fish was done, a randomly collected control
population was kept. Then another group was collected by selecting for big body weight
(experimental group). The differential in the average body weight between experimental
group and control group give the selection difference (S). In the next year the off-spring
of the two groups were obtained by the same method and the fingerlings of control and
experimental groups were reared by communal stocking in the same pond to a
marketable size. The difference in the average body weight between two offspring
groups gives the effectiveness of selection for one generation (R). The heritability was
calculated according to formula:
The data collected during the process of mass selection showed that the number of
experimental fish in each stock was limited due to a limited number of ponds. Even
though the scale of selection is small (Table 3.3) the indices obtained proved to be
acceptable.
Table 3.3. Adjusted average body weight of the common carp in an experiment on
determination of realized heritability in 1988 (Thien and Thang, 1992)
Group of fish Stocking weight (g) Harvesting weight (g)
(150 days)
Weight after adjustment (g)
Experiment 71±4 365±9 335
Control 51±3 286±9 316
h2 =
R
S
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Thus in the first generation the number of fish obtained for mass selection in one of the
stocks was 1720, in each of two other stocks was 400 where as in second generation the
number of fish in each stock was only 250 but the selection differential in second
generation was even higher than that in F1. In the F3 generation field trials, due to
poaching of some stocked fishes the total number of fish obtained for selection was
reduced. So around 33% of fishes in each stock was selected (Table 3.4). It led to
declining of the selection intensity and the selection differential. In the next generations
following the recommendation of some geneticist-selectionists (Kirpichnikov, 1987)
about 20% of fishes was kept to establish the broodstocks. As a result the selection
indices were stabilized at an acceptable level (Fig 3.1).
Figure 3.1. Mass selection of three blood common carp (Thien and Thang, 1992)
Vietnamese (white)
common carp
Hungarian (scale)
common carp
Indonesian (yellow)
common carp
V H Y
HY VY VH
V(HY)
V(HY)
V(HY)
V(HY)
V(HY)
V(HY)
♀V x HY♂ ♀Y x VH♂♀H x YV♂
H(VY)
H(VY)
H(VY)
H(VY)
H(VY)
H(VY)
Y(VH)
Y(VH)
Y(VH)
Y(VH)
Y(VH)
Y(VH)
M A S S S E L E C T I O N
M A S S S E L E C T I O N
M A S S S E L E C T I O N
M A S S S E L E C T I O N
M A S S S E L E C T I O N
F1 (Single)
F1 (Double)
1986
F2 1988
F3 1989
F4 1991
F5 1993
F6 1995
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Table 3.4. Summary data of the mass individual selection of the hybrid stocks of
common carp (V: Vietnamese, H: Hungarian and Y: Indonesian yellow common carp)
(Tran and Nguyen, 1992).
Year Stocks Total Body Indices collected through selection
generation
and place
No. of
fish
weight
(g)
Severity
V (%)
Intensity i
(S/δ )
Differenti
al S (g)
1986
F1
RIA.1
H x (YxV)
V x (YxH)
Y x (HxV)
400
400
1720
162±6
178±4
187±8
12.5
12.5
7.5
2.77
1.66
1.94
99
84
82
1988
F2
RIA.1
H x (YxV)
V x (YxH)
Y x (HxV)
248
258
253
152±7
104±5
148±9
10.1
9.7
9.9
1.76
2.03
1.60
117
177
164
1989
F3
RIA.1
H x (YxV)
V x (YxH)
Y x (HxV)
75
243
74
149±8
155±12
310±16
33.3
32.9
33.8
1.25
0.80
0.77
52
62
41
1991
F4
RIA.1
H x (YxV)
V x (YxH)
Y x (HxV)
200
209
189
260±6
197±5
299±6
20.0
19.1
25.9
1.26
1.75
1.24
74
124
47
1992
F5
RIA.1
H x (YxV)
V x (YxH)
Y x (HxV)
229
235
175
314±12
300±9
350±10
21.8
21.3
22.0
1.28
1.72
1.72
97
69
93
1993
F5
RIA.1
H x (YxV)
V x (YxH)
Y x (HxV)
257
263
243
226±10
300±14
318±11
19.5
20.9
22.6
1.39
1.06
1.44
85
101
114
1995
F6
all stocks Brooders
Average for 5 generations 228 19.8 1.52 93
After five selected generations the common carps of all three stocks have been clearly
improved in growth rate and appearance. However, in order to estimate the genetic gain
it was necessary to know the coefficient of heritability. The data obtained in the
experiments to determine the realized heritability of body weight showed that the
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Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
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indices in the first two generations were suitable for individual selection, but they
decreased from F1 to F4 generation.
In F1 generation the realized heritability was 0.29. In F2 generation experiments, the
results were analysed and adjusted according to the methodology of Wohlfath and Moav
(1972), because of the difference in body weight between two groups of fingerling when
stocked (Table 3.5).
Table 3.5. Heritability (h2) of the body weight of hybrid common carp Hungarian x
(Vietnamese x Yellow) (Tran and Nguyen, 1992).
Generation Parent's body weight (g) Offspring's body weight (g) Heritability
Control
Stock
Selected
Stock
Control
Stock
Selected
Stock
h2=R/S
F1
F2
162±6
218±10
261±9
312±21
180±4
316
209±6
335
+ 0.29
+ 0.20
The realized heritability of body weight was 0.20 for the F2 generation. In the F4
generation this index declined to around 0. In fact, the effectiveness of individual
selection of common carp in the last two generations was low. The experiment to
compare growth rate of carps obtained from breeders in F3 and F5 selected generation
(Table 3.6) showed that the difference in body weight was 7% only. It is expected that
improvement of selection effectiveness in the next phase of the breeding program
should be done by applying another method, for example, family selection.
The average coefficient of realized heritability calculated for each generation was 0.16.
So, based on average index of selection differential, the response to selection for
increasing body weight in each generation could be estimated and it should be around
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Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
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15g or 6.6%. So, the total genetic gain for body weight in the common carp breeding
program after 5 selected generations is estimated to be 33%.
Table 3.6. Growth rate of common carp of the F3 and F5 selected generations in a
grow-out pond; Stocks [Hungarian x (Vietnamese x Yellow)] in Communal stocking in
1995 (Nguyen, 2005).
Generation 6 July
1995
Stocking
18 Aug.
1995
average
5 Oct.
1995
average
16 Nov.
1995
average
14 Dec.
1995
average
9 Feb. 1996
weight
(g)
weight
(g)
weight
(g)
weight
(g)
weight
(g)
Average
(g)
%
F5 15.7 60 170±4 264±7 317±6 409±10 107
F3 15.7 60 170±8 232±7 305±9 382±9 100
The progressive decrease in the genetic gain could be caused by inbreeding. To avoid
inbreeding depression it was recommended to cross among the three stocks to producing
hybrid seed for grow-out farmers. Preliminary data obtained in the experiments
following this direction (Table 3.7) showed that the heterosis effect was present in both
experiments but it was more significant in the experiment No.2.
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Table 3.7. Body weight of common carp in pure stocks and their hybrids reared in the
same pond, 1995 (Thien and Thang, 1992).
No.
Experiment
Stocks and
their hybrids
Stocking
weight (g)
Harvesting
weight (g)
Heterosis effect
g %
H x (VY) 20 365±10 + 21 5.8
1 Y x (HV) 20 377±10 + 9 2.4
Hybrid 19 386±12
H x (VY) 16 367±12 + 127 34.6
2 Y x (HV) 17 415±10 + 79 19.0
Hybrid 17 494±15
3.4 Family selection of common carp
Family selection of common carp has been conducted at RIA1 since 1998, with the
main objective to obtain a common carp line with fast growth and high survival to
improve its production in aquaculture. Using the 5 th generation of common carp from
mass selection as the initial materials, the programme has succeeded in producing two
new generations through induced breeding and rearing of juvenile in hapas. The first
generation, with about 375 brood fish, were selected from the 5 best families (out of 24).
Following up the breeding workplan for the second generation, induced breeding was
undertaken successfully with 40 families of the selected generation and 23 pairs of the
base population. Rearing of juveniles has been carried out entirely in hapas. After
harvest, 2000 fingerlings of the second generation were reared to marketable size for
further selection. In the middle of 2001, fish in the grow-out pond were harvested for
estimation of genetic parameters. Based on breeding value (A), 400 fish (200 females
and 200 males) were selected as brood stock for the third generation of selection.
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Family selection of common carp has been conducted for three years (1998-2000).
Following up the selection plan, the programme has succeeded in selection of the first
generation and from then the second generation have been produced. Selection of
individuals and families in the second generation was undertaken when the size of fish
in growout ponds reached marketable size.
In order to assess the result of selection after two selected generations, the realized
heritability of body weight (h2) at the second selected generation needs to be determined.
These calculations indicated a 5 % increase in growth rate in each selected generation.
3.5 Combination of family and individual selection of common carp
On going selective breeding experiments are using a combination of family and
individual selection. The most recent program utilised six common carp (Cyprinus
carpio L.) lines in this breeding program consisting of: (1), Hungarian 6th generation of
mass selection (2), Yellow 6th generation of mass selection (3), Vietnamese 6th
generation of mass selection (4), Hungarian scale carp (5), Indonesian yellow carp (6).
The brood-fish were 2-3 years old with mean body weight of 1.5-3.0 kg. All the
spawners were healthy, free from disease and deformity.
Broodstock were induced to spawn and gametes were stripped and mixed to create 101
families. These were produced in 3 batches of 12, 38, 51 families, over a 22 day period.
All male and female broodstock were marked by PIT tags (AVID Microchip) to identify
the individuals and family.
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After hatching, the larvae were gathered in fine mesh hapas for nursing. Swim-up fry of
each family were stocked in 1 m3 hapas with the stocking density of 1,000fry/hapa. The
fry were fed daily with the pelleted feed containing 40% crude protein at a rate of 10%
body weight. Rearing period was for 2 months (April-May). Fingerlings of each family
were reared in 5.0 m3 hapas, 500 fry stocked per a hapa. The fry were fed daily with
pelleted feed (30% crude protein) at 7% body weight. Rearing period lasted from May
to June.
As it is known that common carp do not growth well in hapas environment because of
its natural benthic feeding habit the experiment was designed to culture carp in ponds by
tagging fish using Code Wide Tag (CWT). Application of CWT for fingerlings mean
that 5 families could be stock in the same pond with marks at 5 different positions on
tail, abdomen, back, left and right cheek. The growout stage for marked CWT fish was
conducted in earthen ponds by dividing them into units of 120m2 area for each of 500
individuals from 5 families. Fish were grown in these ponds from June to August and
reached 100-150g. Over this time, some families were lost because of low survival rate.
Other families were removed as the morphology such as yellow colour and no scale
phenotype are not preferred by consumer in Vietnam. Position of family tags are
identified by CWT scanner.
It is anticipated that results of these trials will be available very soon. In addition the
RIA1 is still importing new strain from Hungary in an effort to provide better
performing carp strains for small scale farmers (Table 3.8).
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Table 3.8. Current crossbreeding between carp lines to produce 86 families (Nguyen,
2005)
Maternal parent
Paternal
parent
Family
selection,
2nd gener.
Hungarian
6th gener.
H(VY)
Hungaria
n scale
carp
Yellow
6th
gener.
Y(VH)
Indonesia
n Yellow
Vietnamese
line 6th
gener. mass
selection
Family
selection,
2nd gener.
8
9
7
5
1
3
Hungarian
6th gener.
H(VY)
9
7
4
1
2
Hungarian
scale carp
6
4
4
-
Yellow 6th
gener.
Y(VH)
5
3
3
Indonesian
Yellow
3
3
Vietnamese
line 6th
gener. mass
selection
2
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In conclusion, while there has been significant effort to produce genetically improve
carp by Vietnamese government over many years a major concern is the distribution of
seed stock to farmers which may only have been partly successful due to the mixing of
stocks in hatcheries and on farms. Inbreeding depression and undesirable genetic effects
may also be a problem as many farmers report carp growth is slow and fish mature
when they are a small size. Furthermore, the viability of breeding experiment may have
been compromised because pure stocks of experimental common carp strains kept in
separate ponds at RIA1 may have been mixed (A. T. Pham pers.comm).
Thus there are a number of important issues that need to be addressed concerning
Vietnamese common carp stocks including their genetic status and history, the extent of
dissemination of selectively bred stocks and the conservation status of wild stocks.
These issues can be addressed by obtaining molecular genetic information which can
provide insights into genetic diversity and therefore, inbreeding and the extent of stock
mixing in both cultured and wild stocks. In addition, molecular genetic data can
contribute to the resolution of issues relating to the taxonomy, evolution, and
biogeography of common carp and help identify genetically divergent wild stocks of
conservation significance.
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4. Overview molecular genetic studies on common
carp in the world
Because it is one of the most important farmed freshwater fish in the world, common
carp have been subject of numerous molecular genetic studies. The foci of these studies
have been questions relating to phylogenetics, population structure, taxonomy and
aquaculture and the impact of domestication.
In the past, traditional protein markers had been used to study the genetics of common
carp populations on regional levels. For instance, allozyme information is available for
domesticated and wild population culture and samples in Hungary (Csizmadia et al.,
1995), Czech Republic (Desvignes et al., 2001; Slectova et al., 2002), Uzbekistan
(Murakaeva et al., 2003), Italy (Cataudella et al., 1987), Japan (Macaranas et al., 1986),
Indonesia (Sumantadinata and Taniguchi, 1990), Israel (Ben-Dom et al., 2000), Estonia
(Paaver and Gross, 1991), Poland (Anjum, 1995), Germany (Kohlmann and Kersten,
1999) and Australia (Davis et al., 1999). More recently mitochondrial DNA (Davis et al.,
1999; Froufe et al., 2002; Mabuchi et al., 2005; Zhou et al., 2003), microsatellite
(Bartfai et al., 2003; David et al., 2001; Desvignes et al., 2001; Lehoczky et al., 2005;
Tanck et al., 2000), RADP (Bartfai et al., 2003; Wang and Li, 2004), and AFLP data
(David et al., 2001) have been used to examine genetic variation in common carp
populations.
To date, there are few studies of common carp populations across its full geographical
range in Eurasia. Those studies that have been conducted have not sampled
comprehensively, but nevertheless suggest that carp may be divided into European and
Asian groups (Brody et al., 1979; Kohlmann et al., 2003; Kohlmann et al., 2005);
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Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
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although this interpretation is not consistent with the actual data presented in some
studies (Kohlmann et al., 2005).
The complete mitochondrial DNA nucleotide sequence of common carp was described
by Chang et al. (1994) (GenBank accession number: X61010). This helped provide
primers for sequencing mitochondrial DNA genes and fragments which is more and
more popularly used to investigate relationships of common carp strains or populations.
For example, the molecular phylogeny of three subspecies of common carp in China
was analysed by Zhou et al. (2004b) using sequence of Cytochrome b (Cyt b) and
control (CR) gene regions. Mabuchi et al. (2005) discovered a genetically divergent
form of common carps from Lake Biwa, using mitochondrial DNA CR sequence data.
Phylogenetic relationships of ornamental (koi) carp, Oujiang color carp and Long-fin
carp were analysed by Wang and Li (2004) using mitochondrial DNA cytochrome c
oxidase subunit II (COII) gene sequences.
Currently there are several published studies of common carp that give primers for
microsatellite loci (Crooijmans et al., 1997; Sun and Liang, 2004; Yu and Guo, 2004).
Thirty two microsatellite markers of poly (CA) type in common carp were described by
Crooijmans et al. (1997). While these authors stated that these loci will be valuable as
genetic marker for use in population genetic, breeding and evolution studies, they did
present any population genetic analyses (Kohlmann et al., 2005; Lehoczky et al., 2005;
Zhou et al., 2004a). Kohlmann et al. (2003; 2005) have presented the only population
genetic studies of common carp using four microsatellite loci and found significantly
greater variation than was apparent from allozyme studies.
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Studies of QTLs in common carp are limited. There is only one gene linkage map of
common carp which mapped of loci associated with cold tolerance (Sun and Liang,
2004), using the segregation of 272 markers, including 105 gene markers, 110
microsatellites, and 57 RAPD markers. Despite the large number of genetic studies of
common carp, none have addressed genetic diversity and genealogical relationships on a
global basis. Views on the taxonomy and origin of carp are questionable and require
detailed investigation. In addition the study of common carp from certain regions have
been neglected, including Vietnam (south East Asia), which is home to indigenous
common carp that have not been examined using modern molecular genetic methods to
any significant extent.
Fish breeding practices and stock improvement strategies in Vietnam in relation to common carp
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5. Genetic diversity of common carp in Vietnam using
direct sequencing and SSCP analysis of the DNA
control region
Common carp is one of the main aquaculture species in Vietnam (Nguyen and Ngo,
2001) and is cultivated along with Chinese carp and Indian carp in polyculture ponds
and rice-fields. Thesis species together makes up one of the most important food and
income resources in rural communities in Vietnam (Edwards et al., 2000). The
enhancement of common carp production in Vietnam has focused substantially upon the
development of genetically improved strains (Tran and Tran, 1995). For this purpose,
Hungarian and Indonesian carp strains were imported into Vietnam almost 30 years ago
for crossbreeding and mass selection programs with local Vietnamese carp.
The genetic improvement strategy adopted for common carp in Vietnam involved the
development of hybrid common carp by crossbreeding among three genetic lines
(Vietnamese white, Hungarian scale and Indonesian yellow common carp) coupled with
mass selection.
The ongoing development of farmed common carp stocks in Vietnam requires that
several important issues are addressed. These included the possibility that: (1) stocks of
experimental or genetically improved lines have become mixed with other stocks in
ponds at Research Institute for Aquaculture No 1 (RIA1) or provincial hatcheries; (2)
distribution of these lines as seed stock or broodstock to regional hatcheries or farms has
been ineffective in increasing genetic diversity, and (3) reduction in effective population
sizes (Ne) in genetically improved or hatchery maintained stocks has occurred, leading
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Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
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to loss of genetic variation, gene frequency changes and possibly inbreeding depression.
This last possibility is consistent with reports by many farmers of slow growth and early
maturity in their cultured stocks of common carp (T. A. Pham, personal
communication).
In addition to the genetically improved lines of common carp produced at RIA1, eight
local varieties have been recognised in Vietnam with reported useful features for culture
and for marketing (Bakos and Gorda, 2001). There is now the possibility that distinct
wild common carp stocks are in decline because of excessive harvesting and
interbreeding with introduced common carp strains (Nguyen and Ngo, 2001). Therefore,
it is important to identify and characterise genetically distinct local varieties of cultured
fish for conservation purposes in general and specifically for common carp populations
(Mabuchi et al., 2005; Murakaeva et al., 2003).
A wide range of molecular marker systems have been used to study genetic diversity in
aquaculture species (Chen et al., 2004; Diniz et al., 2005; Garoia et al., 2004; Sato et al.,
2005; Sotka et al., 2005; Valles-Jimenez et al., 2004; Yu and Guo, 2004). As one of the
most important aquaculture species in the world, genetic variation in carp has been
examined in many parts of the world using microsatellites (Desvignes et al., 2001;
Kohlmann et al., 2005), RAPDs (Bartfai et al., 2003), AFLPs (David et al., 2001),
allozymes (Kohlmann and Kersten, 1999), RFLPs (Gross et al., 2002; Zhou et al., 2003)
and direct sequencing of mtDNA fragments (Froufe et al., 2002; Zhou et al., 2004b).
While these have included studies of both European and Asian common carp so far
there have been no detailed studies of molecular genetic variation in common carp in
Vietnam nor has the technique of Single Strand Conformation Polymorphism (SSCPs),
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which is being increasingly used to assay for genetic variation in fish species (Aurelle
and Berrebi, 2001; Liu and Cordes, 2004), been applied to common carp.
5.1 Objective
In this study, we investigate genetic diversity of Vietnamese common carp strains and
populations by using direct DNA sequencing and SSCP analysis of the mtDNA CR .
This region of the mtDNA molecule was chosen because it has a very high nucleotide
substitution rate, making it particularly useful for estimating the genetic population
structure of closely related animal populations (Sivasundar et al., 2001; Vigilant et al.,
1991). These data are then used to examine a range of questions relating to genetic
diversity and management of wild and domesticated populations of common carp in
Vietnam.
5.2 Materials and Methods
5.2.1 Sample collection
Common carp were collected in 2003 and 2004 from broodstock populations
maintained by eleven hatcheries, three experimental common carp lines maintained at
RIA1, and by sampling six wild populations, using seine and lift nets. Samples of
common carp strains from China, Indonesia, Japan, Hungary and India were obtained
for comparative purposes. Tissue samples were taken as fin clips and preserved in 90%
ethanol. Locality and sample size details are provided in Table 5.1 and Fig 5.1.
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Table 5.1. Location, code and number of samples sequenced and analysed by the SSCP
technique.
Population Code Location Type
Sequencing SSCPs
Hungarian scale-RIA11 HUS Tu Son, Bac Ninh, Vietnam E 4 50
Indonesian yellow-RIA1 IDY Tu Son, Bac Ninh, Vietnam E 6 50
Vietnamese white-RIA1 VNW Tu Son, Bac Ninh, Vietnam E 4 50
Vinh Phuc VIP Me Linh, Vinh Phuc, Vietnam H 4 50
Thai Nguyen THN Cu Van, Thai Nguyen, Vietnam H 3 50
Son La SOL Son La town, Son La, Vietnam H 4 50
Bac Kan BAK Bach Thong, Bac Kan, Vietnam H 6 50
Tuyen Quang TUQ Hoang Khai, Tuyen Quang, Vietnam H 4 50
Yen Bai YEB Van Chan, Yen Bai, Vietnam H 3 50
Hoa Binh HOB Hoa Binh town, Hoa Binh, Vietnam H 6 50
Ha Tinh HAT Duc Long, Ha Tinh, Vietnam H 4 50
Can Tho CAT Cai Rang, Can Tho, Vietnam H 4 36
Sai Gon SAG Binh Chanh, Sai Gon, Vietnam H 4 35
Thac Ba Reservoir TBR Yen Binh, Yen Bai, Vietnam H 3 50
Bang Giang River BGR Cao Bang town, Cao Bang, Vietnam W 6 50
Lo River LOR Yen Son, Tuyen Quang, Vietnam W 4 50
Red River RER Van Giang, Hai Hung, Vietnam W 4 50
Lam River LAR Nam Dan, Nghe An, Vietnam W 3 50
Son River SOR Bo Trach, Quang Binh, Vietnam W 4 47
Dak Lak DAL Ea Kao, Dak Lak, Vietnam W 4 50
Xingguonensis XIG Jaing xi China 3 5
Wananensis WAN Jaing xi China 3 5
Wuyuanensis WUY Jaing xi China 3 5
Color COL Jaing xi China 3 5
Red Koi REK Komaki Japan 3 21
Wild Amur WAR Karnataka, India 3 5
Majadanu MAJ Sukamandi, Indonesia 3 5
Rajadanu RAJ Sukamandi, Indonesia 3 5
Widan WID Sukamandi, Indonesia 3 5
GenBank GBK Taiwan2 1
Goldfish GOF Unknown 1
Population size (n)
1 Research Institute for Aquaculture No 1; 2 Origin of sample not provided; E:
Experimental group; H: Hatchery group; W: Wild group
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Figure 5.1. Collection localities for Cyprinus carpio L. samples in Vietnam
5.2.2 DNA extraction and sequencing of control region
The total genomic DNA was extracted using the protocol from Crandall et al. (1999).
Between three and six individuals from each populations or strain were first analysed by
direct sequencing. The mitochondrial CR was amplified using primers Carp-Pro (5’
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AAC TCT CAC CCC TGG CTA CCA AAG 3’) and Carp-Phe (5’ CTA GGA CTC
ATC TTA GCA TCT TCA GTG 3’) designed from the common carp whole
mitochondrial genome sequence (GenBank, AC: X61010). PCR was carried out in 50 µl
reactions volumes (1 X reaction buffer, 2 mM dNTP, 1.5 mM MgCl2, 0.5 µM of each
primer, 0.5 units Taq DNA polymerase, and approximately 200 ng DNA template).
Thermal cycling comprised 95 oC for 3 min, followed by 34 cycles of 95 oC for 30 s,
annealing at 55 oC for 30 s, and an extension temperature of 72 oC for 1 min. This was
then followed by a final extension of 72 oC for 3 min. PCR products were purified using
the QIA quick PCR purification kit (Qiagen Hiden Germany), following ABI PRISM
BigDye Terminator (Foster city, CA, USA) sequencing protocols. For each individual,
sequencing reactions were performed using both forward and reverse primers, resulting
in a consensus fragment of 745 bp in length.
5.2.3 Single Strand Conformation Polymorphism (SSCP) amplification
A short highly variable fragment of the CR was selected from the common carp
sequences obtained as described above. This fragment was approximately 230 bp and
was amplified by the primers F1 (5’ GCA GGT ACA TAA TAT TAA 3’) and R1 (5’
CAG ATG CCA GTA ATA ATT 3’). PCR was carried out in 10 µl reaction volumes (1
X reaction buffer, 2mM dNTPs, 1.5mM MgCl2, 0.5µM of each primer, 0.1 units Taq
DNA polymerase, and approximately 10ng DNA template). Thermal cycling comprised
94 oC for 3 min followed by 34 cycles 94 oC for 20 s, annealing at 55 oC for 20 s, and an
extension temperature of 72 oC for 50 s, followed by a final extension of 72 oC for 3
min. PCR product size was estimated using the Promega DNA/Hae III marker.
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To obtain SSCP phenotypes, PCR product (1µl) was added to 7 µl of loading buffer
(99% formamide, 1mM NaOH, 0.2% w/v bromophenol blue and xylene cyanol),
denatured for 2 min at 94 oC and placed directly on ice. Samples were loaded onto an
8% polyacrylamide (37.5: 1 acrylamide-bisacrylamide) gel (16 cm long, 1.5 mm thick)
containing 5% glycerol and 0.5 X TBE, and run at 5W for 12h at 4 oC. SSCP products
were visualised by silver staining using the method of Mirol et al. (2002). The resultant
bands were scored by comparison with five standard carp haplotypes (representing the
five most frequently encountered haplotypes), which were included on each gel for
reference. Rare haplotypes were subsequently run side by side to ensure they were
correctly scored.
5.2.4 Data analysis
Nucleotide (π) and haplotype diversity (h) were calculated from the sequence data using
DNASP 4.10 (Rozas et al., 2003). Sequences were aligned using the program Clustal X
(Thompson et al., 1997). The most suitable model of evolution was obtained using
Modeltest 3.06 (Posada and Crandall, 1998). This model was used to calculate pairwise
sequence distances between haplotypes and for the construction of a Neighbour-Joining
dendrogram (NJ) using PAUP*4.0b.10 (Swofford, 2000). Confidence levels in the
resulting relationships were assessed using the bootstrap procedure with 1,000
pseudoreplicates (Swofford, 2000). The corresponding control region sequence for
common carp from GenBank (Chang et al., 1994) was included in the data set for
comparative purposes, and the Carassius auratus control sequence (GenBank accession
NC_002079) was used as the outgroup.
For the SSCP data set, haplotype diversity for each population was calculated using
ARLEQUIN (Scheneider et al., 2000). Genetic divergence between samples was
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Christopher M Austin, Tuan Anh Pham, Binh Thanh Thai, Hung Quang Le, Tan Thi Nguyen
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estimated by pairwise Fst analysis using the same program. Patterns of overall genetic
relationships among populations were summarised using UPGMA clustering of Roger’s
(1972) genetic distance as implemented in TFPGA (Miller, 1997). Multidimension
scaling (MDS) was performed on matrices of genetic distance to test for the presence of
nonhierarchical patterns of relationships among populations using SPSS 10.0. The
partitioning of genetic diversity within and between populations and populations
grouped according to origin (experimental line, hatchery and wild), was undertaken by
an analysis of molecular variance (AMOVA) for binary data, using the GenALEX add-
in for Microsoft Excel (Peakall and Smouse, 2001). Multiple comparisons were
subjected to sequential Bonferroni correction to control the Type I error rate (Rice,
1989).
5.3 Results
5.3.1 Control region sequences and SSCP variation
Sequences for a 745 bp fragment of the mtDNA CR were obtained from 111 fish
representing 41 populations or strains. A total of 19 haplotypes with 78 variable and 30
phylogenetically informative sites were identified. The nucleotide composition was A +
T rich (A= 31%; T= 32%), and variation consisted predominantly of transitions (Ti : Tv
= 2.56). All sequences have been deposited in GenBank (AC: AY597942-AY597976;
DQ354144-DQ354149).
Vietnamese carp populations have high haplotype diversity (mean = 0.92±0.02), but
low nucleotide diversity (mean = 0.01±0.00). The most divergent Vietnamese
haplotypes differed by only 9 base pairs. Diversity and relationships among haplotypes
are depicted in Fig 5.2 together with the 14 corresponding SSCP phenotypes determined
from the shorter (230 bp) fragment. From this figure it can be seen that the SSCP
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technique was successful in resolving a significant proportion of the nucleotide
variation detected in sequencing the longer control fragment. It is noteworthy that four
of these haplotypes allow the discrimination of Vietnamese white (haplotype C),
Hungarian (haplotype A) and Indonesian yellow (haplotypes B & D) carp strains from
RIA 1. In addition, common carp samples from China (haplotypes I & R) and
Indonesian (haplotypes B, D &J) and Koi carp (haplotype L) were all distinguishable
from Vietnamese carp.
The summary of relationships among control haplotypes (Fig 5.2) shows that, apart
from two of the Chinese strains, which share the same haplotype, and are quite
divergent from the other carp samples, there are a large number of haplotypes that are
closely related to each other. Minor exceptions are the Hungarian carp haplotype (A)
and a haplotype found in Bak Kan and Dak Lak (haplotype E), the Bang Giang River
(haplotype F) and the Lo River (haplotype G) and Koi carp (haplotype L).
A total of 968 individuals from both wild and hatchery populations were scored for
SSCP variation. In addition to the non-Vietnamese strains that had seven
distinguishable SSCP phenotypes, five SSCP haplotypes were distinguishable among
Vietnamese common carp samples. Comparison with the nucleotide sequences revealed
that these SSCP haplotype differ by 3-8 bp. Haplotype frequencies and diversity
estimates are summarized in Table 5.2 for 20 common carp populations. Three
haplotypes, Hungarian (A), Indonesian (B) and Vietnamese (C), predominated in
common carp samples and five (D, E, F, G and H) were relatively rare or occurred only
at low frequencies. Intra-population diversity varies widely among the populations
ranging from populations with a single haplotype (h =0) to six haplotypes (h = 0.55).
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The experimental strains from RIA1 have the lowest diversity (h= 0-0.28), the hatchery
stocks with the exception of Thai Nguyen, have high diversity (h = 0.49-0.64) and the
wild stocks have an intermediate level of diversity (h = 0.26-0.41) (Table 5.2).
The three experimental strains from RIA1 are also highly differentiated from each other.
The Hungarian scale strain is fixed for haplotype A, the Indonesian yellow strain is
dominated by haplotype B (84%), while the Vietnamese white strain in dominated by
haplotype C (94%). All three of these haplotypes are found in almost all hatchery and
wild carp populations, however in the Vietnamese white strain haplotype C dominate
(55%) followed by the predominate Indonesian haplotype B at 25% and the Hungarian
haplotype A at 12%.
The six wild common carp populations (RER, LOR, LAR, SOR, DAL, and BGR) have
generally similar haplotype profiles and like the Vietnamese experimental strain,
haplotype C predominates. Six of the hatchery stocks have haplotype profiles largely
similar to the wild populations (haplotype C = 0.52-0.94). The five other hatchery
samples, in contrast, have haplotype profiles dominated by the Indonesian haplotype B
(0.50-0.84), although it is noteworthy that they also all possess the Vietnamese
haplotype C, albeit at a lower frequency (0.04-0.39). Interestingly, almost all hatchery
and wild samples have the Hungarian haplotype (A
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