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Genetics for Fisheries
Resource Conservation
Presented to:-
Dr.K.Karal Marx,
Dean,IFPGS,TNJFU,
OMR Campus,Chennai.
Introduction
• Conservation of fish genetics resources is critical to aquatic
biodiversity. World stocks of fish and shellfish have been and
continue to be the principal gene banks for aquaculture.
• In plants and mammals, cryopreserved gene banks have been
established as the total genetics complement can be
preserved in a dormant,chilled,frozen state. In fish, it has not
been possible to cryopreserve ova, so at present only frozen
milt can be stored. This necessitates some live fish being
maintained to provide a source of eggs.
• The majority of fish and shellfish are harvested from
populations that live in natural environments. over
harvesting in these areas coupled with pollution,
environmental degradation and loss of habitat raise the
potential for significant depletion or loss of important fish
resources.
Cont ...
• conservation of aquatic diversity is imperative for
sustainable management of fisheries resource;
• Sustainability is essential for security of protein-rich food
and medically and commercially important raw materials
from aquatic ecosystems.
• two processes by which genetic resources are lost; these are
(1) the extinction of a species and
(2) the reduction of genetic variation within a species.
• The former process, once it occurs, is qualitative, final and
irreversible.
• The latter process is a matter of degree is to some extent
reversible.
• Aquaculture is still in a relatively early stage of development and
the production of new strains and races of food fishes will
require careful management of available genetic resources.
Why required Genetics Resource
conservation in Fish?
• Nutritional arguments for Genetic Resource
Preservation
• Economic arguments for Genetic Resource Preservation
1) Substances isolated from fish and other aquatic animals are
already widely used in medical research.(For example,
tetradotoxin (TTX), a toxin isolated from the puffer fish).
2) A research tool is luminescent proteins. For example,
Aqueorin from a jellyfish species has been widely used to
monitor the Ca2+ concentration in cells.
• Ecological arguments for Genetic Resource Preservation
LEVELS AND METHODS OF GENETIC RESOURCE
PRESERVATION IN FISH
1. Human Impacts on Aquatic Habitats
• In continental waters the same effects can occur but
often to a much greater degree and whole populations
can become extinct, solely through over-fishing.
• The introduction of exotic species may also be included
as a factor of importance to endemic fish populations.
• Another serious human impact is the disruption of
biological (in most cases reproductive) cycles in fish
populations as a consequence of building dams or other
obstructions on rivers where migratory species occur.
Dams may not only prevent the migration to upstream
spawning grounds, but they may also change rivers into
semi-lacustrine habitats quite unsuitable for stream
species. Ecological barriers are also common and may be
caused by zones of pollution in the lower reaches of rivers
preventing the migration of various species.
• The conservation of the genetic resources of fish, four
main levels of concern and strategy can be identified
Level Potential Genetic
Problems
Methods
Oceanic fisheries Sub-population
extinction
Tagging and
monitoring
Continental habitats Species extinction Establish reserves
Genetic erosion Scientific management
of
reserves
Restocking
Aquaculture Genetic erosion Controlled breeding
Inbreeding depression Hybridization
Loss of fitness Cryopreservation
Stock enhancement Genetic erosion Controlled breeding
Inbreeding depression Hybridization
Loss of fitness Cryopreservation
GENERAL PRINCIPLES OF GENETIC
RESOURCE CONSERVATION
• The Importance of Genetic Variation
• Genetic variation is a measure of a population's ability to adapt
to environmental change or stress, and thereby to survive.
• some fish species, individuals possessing the most genetic
variation have been shown to have better survival rates or higher
relative growth rates. Relatively heterozygous individuals appear
to be more resistant to environmental perturbations during
development. Clearly, genetically variable populations have
many advantageous characteristics that are absent from
genetically impoverished ones.
• Effects of Inbreeding
• The selection of small numbers of parents can reduce genetic
variability. This leads to generation after generation of
inbreeding of closely related individuals which very often results
in homozygosity for unfavorable genes. The overall result is
inbreeding depression.
• Monitoring and Measuring Genetic Variation
• Traits such as color patterns are typically controlled by a
small number of genes (one to three).
• Electrophoresis of proteins has been widely applied for the
direct study of genetic variation in fish populations. The
importance of electrophoresis to the study of fish genetics
resides in the ability to directly estimate genetic relationships
from its results, and also because variation of
electrophoretically detectable genes is often correlated with
variation of other genes. To the extent that such a correlation
is widespread among fish species, electrophoretic variation
can be a general estimator of genetic variation.
• There are situations in which it may be desirable to
electrophoretically estimate genomic variability and then to
use these data as a base-line for comparing the genetic
effects of a particular pattern of stock breeding or
exploitation.
• Population Genetic Structure in Relation to
Exploitation and Extinction
• Fishes probably surpass all vertebrate groups in their variety of
social structures and kinds of life histories. It is not surprising
therefore that some controversy has arisen regarding the
significance of such variables as population structure, dispersal,
and genetic drift, particularly with regard to genetic integrity of
populations.
• Population structure is thus a useful guide for a priori
priority ranking with regard to genetic resource conservation ,
at least with regard to the extinction potential of local
populations.
• Geographic range alone is quite useful. The majority of
species which reproduce in estuaries, river systems in the
temperate zones, and in coastal pelagic zones are relatively
widely distributed and fairly numerous.
• Species residing in tropical floodplain rivers, extreme
environments such as shallow desert lakes or salt lakes may
be far less numerous and typically have rather limited
geographic ranges.
CRITERIA FOR MINIMUM POPULATION
SIZES
• Criteria and Time Scale
• The establishment of minimum viable population sizes
is one of the principal goals of conservation genetics.
Other important criteria would include the demography
and life history of the species, and certain ecological
variables, for example, the probability and severity of
catastrophe.
• fishes living in shallow bodies of water in regions
subject to extreme drought are likely to have a high
probability of extinction. Also, they may go through
severe bottlenecks with significant frequency .
• At the opposite extreme, deep sea species are unlikely
to be exposed to physical events which bring about a
collapse in population size.
• The “time scale of survival” is a useful device
for structuring a discussion of preserving
genetic variation. Somewhat arbitrarily, there
are three problems or issues:
1. a short-term issue is immediate fitness –
the maintenance of vigor and fecundity during an interim
holding operation, usually in an artificial environment, such as
when breeding domesticated or semi-domesticated fish stocks.
(If, however, breeding is expected to continue for more than Ne
generations, the programmed, in effect, becomes a long-term
operation.)
2. the long-term issue is adaptation –
the persistence of vigor and evolutionary adaptability of
a population in the face of a changing environment;
3. the third issue is evolution in the broadest sense, i.e.,
speciation, or the creation of evolutionary novelty (Soule,
1980). For our purposes, the first and second issues are
the most relevant and the third is the least relevant.
• Survival of Captive Populations
• Population Influences on Effective Population Size
• The Maintenance of Long-term Fitness
• Franklin (1980) argues that a minimum effective
size of 500 is needed to preserve useful genetic
variation, because:
1.The relevant phenotypic traits in conservation are
quantitative (polygenic). For such traits the average
effect of a gene is small, and most of the genetic
variation is additive.
2. Weak directional or stabilizing selection does not
erode additive genetic variation at a significant
rate;
3. The significant evolutionary forces, therefore, are
mutation, and genetic drift. That is, if a population
is below some threshold size, it loses variation by
drift at a faster rate than it gains variation by
mutation.
THE COMPONENTS OF GENETIC
IMPOVERISHMENT IN FISH
POPULATIONS
Pollution Fishing pressure
Sport fishing
Artificial selection
Reproductive
isolation
Techniques For The Conservation And Enhancement Of
Genetic Resources In Closely Managed Fish
Populations
1.Artificial Selection of Broodstock
• Artificial selection of broodstock is broadly defined as the
conscious selection of an individual or genetic group for the
purpose of providing progeny for culture or stock
enhancement.
• This selection can be based upon the performance of an
individual (individual selection), of its progeny (progeny
selection), of its ancestors (pedigree selection), of its
contemporary relatives or on the potential of a useful
combination with a parent of another genotype (hybridization
selection).
• In all cases selection is practiced in order to improve the
performance of the progeny group above that of a progeny
group from unselected parents.
2.Artificial Methods of Reproduction
• Methods of artificial propagation, including the use of
hormones, in vitro fertilization and development, are in
wide use in aquaculture.
• The ways in which artificial propagation can affect
the maintenance and study of genetic variation
include:
1. Increase of genetic variability and genetic
understanding.
2. Aids in the conservation of stocks, strains, species
and other genetic groups.
3. Allows the development and use of specialized
breeding methods.
4. Allows the efficient maintenance of effective
population size.
5. Aids in interspecific hybridization.
3.Hybridization and Heterosis
• Hybridization (or cross breeding) can be divided into two
categories:
(1) intraspecific: crosses between strains, stocks, land
races, geographic populations within a species;
(2) interspecific: crosses between species.
• Hybridization is practiced to achieve either of two
favorable outcomes. These are:
• (1) heterosis or hybrid vigor, which is defined in a
broad sense as an increased performance or value (to
the aqua breeder) of progeny above the average of the
parental performances or value,
• (2) non-heterotic effects which is the performance of
the progeny as the result of simple combination of
parental genotypes.
4.Enhancement of stocks
• The concept of augmentation of natural population
production by introduction of hatchery raised, “cultured”
juvenile fishes into natural systems. Varying levels of success
have been achieved.
• It is apparent that natural fish stocks undergo genetic
alteration through addition and deletion of genetic material.
Although quite a lot of attention has been given to effects of
competition between “wild” and hatchery raised fish.
• Stock enhancement through ranching is feasible only(1)if
there is incomplete colonization of available habitat by
juveniles and (2) if the trophic capacity of the habitat is
under-utilized by a stock/its competitors. i.e. there is
available carrying capacity
• The successful induced spawning and larval rearing of
endangered Hilsa , N chitala , H nigricollaris have opened up
the avenues of ranching their advanced fingerlings in
depleted water bodies for stock replenishment.
5 Cryopreservation of Genetic
Resources
• the genetic resources for
(1) cultured fish stocks,
(2) unique natural populations,
(3) species that are threatened.
At present methods for freezing fish eggs or embryos
are not technically feasible but research in that
area is being actively pursued (e.g., Whittingham
and Rosenthal, 1978).
6. By using different CHROMOSOME
ENGINEERING Techniques
• Gynogenesis:-
• Androgenesis:-
• Production of diploid, triploid, tetraploid fish production:-
• Production of YY stocks:-
• Transgenic fish production:-
• Cross breeding:-
In- situ conservation Ex-situ conservation
1.The threatened species
are conserved outside
their natural habitats.
a. Live gene bank
b. Gene bank with
gamete,
c. Gene bank with DNA
1. Continued co-evolution
where in the wild
species may continue to
co-evolve with other
forms providing the
breeders with a dynamic
source of resistance that
is lost in ex situ
conservation
2. National parks and
biosphere reserves may
provide less expensive
protection for the wild
relatives than ex situ
Live gene bank
• In a live Gene Bank which is a Genetic Resource Centre, the
endangered species are reared in captivity, bred therein and
genetically managed avoiding inbreeding depression,
domestication and unintended selection. The NBFGR is
maintain the wild stocks of threatened species N chitala, C
marulius, Tor putitora in the Mini germplasm Repository.
• Gene bank with DNA:-
• DNA banking which is yet to be initiated would include
1. Genomic DNA
2. DNA Library( Genomic DNA or cDNA library)
3. Cloned DNA fragments.etc
Constraints to management and
conservation of aquatic genetic
resources
1. Inadequate knowledge base:
• The knowledge base for managing the genetic
resources of aquatic species in inadequate. Although
sufficient information is available for a few intensively
studied and managed species, such as
salmoinds,tilapia and carp, there is paucity of even
basic biological information for most of the rest.
Nothing is known of their genetics. In fact, genetic
research on aquatic animals has not been considered a
high priority.
2. Insufficient attention
3. Magnitude of the task
Recommendation
1.Conservation of genetic diversity must be an integral
part of policies and programmers that affect aquatic
animal resource development.
2. Maintenance of the genetic diversity of aquatic animal
species should be considered when management and
exploitation practices are developed .
3. The introduction and transfer of aquatic species should
be regulated strictly by governments and should not be
permitted without careful analysis of the potential
ecological, biological, and genetics risks.
Reference
• Allendorf, F.W. and F.M. Utter, 1979 Population genetics. In Fish
physiology, edited by W.S. Hoar, D.J. Randall and J.R. Brett.
New York, Academic Press, vol.8:407–54
• Bakos, J., Z. Krasznai and T. Marian, 1978 Crossbreeding
experiments with carp, tench and Asian phytophagous cyprinids.
Aquacult.Hung., Szarvas, 1:51–7
• Falconer, D.S., 1960 Introduction to quantitative genetics.
London, Oliver and Boyd
• Frankel, O.H. and M.E. Soule, 1981 Conservation and evolution.
London, Cambridge University Press
• Helsop-Harrison, J., 1974 Genetic resources conservation: the
end and the means. J.R.Soc.Arts, Feb.issue:157 p.
• Horton, H.F. and A.C. Ott, 1976 Cryopreservation of fish
spermatozoa and ova. J.Fish.Res.Board Can., 33(4) Part 2:995–
1000
• W S Lakra, A Gopalkrishnan,.2013,Genetic,Genetic Engineering
and Biotechnology in Fisheries,9.cryopreservation and Fish
diversity Conservation,165-171
Genetics for fish_resource_conservation_new_krik[1]

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Genetics for fish_resource_conservation_new_krik[1]

  • 1. Genetics for Fisheries Resource Conservation Presented to:- Dr.K.Karal Marx, Dean,IFPGS,TNJFU, OMR Campus,Chennai.
  • 2. Introduction • Conservation of fish genetics resources is critical to aquatic biodiversity. World stocks of fish and shellfish have been and continue to be the principal gene banks for aquaculture. • In plants and mammals, cryopreserved gene banks have been established as the total genetics complement can be preserved in a dormant,chilled,frozen state. In fish, it has not been possible to cryopreserve ova, so at present only frozen milt can be stored. This necessitates some live fish being maintained to provide a source of eggs. • The majority of fish and shellfish are harvested from populations that live in natural environments. over harvesting in these areas coupled with pollution, environmental degradation and loss of habitat raise the potential for significant depletion or loss of important fish resources.
  • 3. Cont ... • conservation of aquatic diversity is imperative for sustainable management of fisheries resource; • Sustainability is essential for security of protein-rich food and medically and commercially important raw materials from aquatic ecosystems. • two processes by which genetic resources are lost; these are (1) the extinction of a species and (2) the reduction of genetic variation within a species. • The former process, once it occurs, is qualitative, final and irreversible. • The latter process is a matter of degree is to some extent reversible. • Aquaculture is still in a relatively early stage of development and the production of new strains and races of food fishes will require careful management of available genetic resources.
  • 4. Why required Genetics Resource conservation in Fish? • Nutritional arguments for Genetic Resource Preservation • Economic arguments for Genetic Resource Preservation 1) Substances isolated from fish and other aquatic animals are already widely used in medical research.(For example, tetradotoxin (TTX), a toxin isolated from the puffer fish). 2) A research tool is luminescent proteins. For example, Aqueorin from a jellyfish species has been widely used to monitor the Ca2+ concentration in cells. • Ecological arguments for Genetic Resource Preservation
  • 5. LEVELS AND METHODS OF GENETIC RESOURCE PRESERVATION IN FISH 1. Human Impacts on Aquatic Habitats • In continental waters the same effects can occur but often to a much greater degree and whole populations can become extinct, solely through over-fishing. • The introduction of exotic species may also be included as a factor of importance to endemic fish populations. • Another serious human impact is the disruption of biological (in most cases reproductive) cycles in fish populations as a consequence of building dams or other obstructions on rivers where migratory species occur. Dams may not only prevent the migration to upstream spawning grounds, but they may also change rivers into semi-lacustrine habitats quite unsuitable for stream species. Ecological barriers are also common and may be caused by zones of pollution in the lower reaches of rivers preventing the migration of various species. • The conservation of the genetic resources of fish, four main levels of concern and strategy can be identified
  • 6. Level Potential Genetic Problems Methods Oceanic fisheries Sub-population extinction Tagging and monitoring Continental habitats Species extinction Establish reserves Genetic erosion Scientific management of reserves Restocking Aquaculture Genetic erosion Controlled breeding Inbreeding depression Hybridization Loss of fitness Cryopreservation Stock enhancement Genetic erosion Controlled breeding Inbreeding depression Hybridization Loss of fitness Cryopreservation
  • 7. GENERAL PRINCIPLES OF GENETIC RESOURCE CONSERVATION • The Importance of Genetic Variation • Genetic variation is a measure of a population's ability to adapt to environmental change or stress, and thereby to survive. • some fish species, individuals possessing the most genetic variation have been shown to have better survival rates or higher relative growth rates. Relatively heterozygous individuals appear to be more resistant to environmental perturbations during development. Clearly, genetically variable populations have many advantageous characteristics that are absent from genetically impoverished ones. • Effects of Inbreeding • The selection of small numbers of parents can reduce genetic variability. This leads to generation after generation of inbreeding of closely related individuals which very often results in homozygosity for unfavorable genes. The overall result is inbreeding depression.
  • 8. • Monitoring and Measuring Genetic Variation • Traits such as color patterns are typically controlled by a small number of genes (one to three). • Electrophoresis of proteins has been widely applied for the direct study of genetic variation in fish populations. The importance of electrophoresis to the study of fish genetics resides in the ability to directly estimate genetic relationships from its results, and also because variation of electrophoretically detectable genes is often correlated with variation of other genes. To the extent that such a correlation is widespread among fish species, electrophoretic variation can be a general estimator of genetic variation. • There are situations in which it may be desirable to electrophoretically estimate genomic variability and then to use these data as a base-line for comparing the genetic effects of a particular pattern of stock breeding or exploitation.
  • 9. • Population Genetic Structure in Relation to Exploitation and Extinction • Fishes probably surpass all vertebrate groups in their variety of social structures and kinds of life histories. It is not surprising therefore that some controversy has arisen regarding the significance of such variables as population structure, dispersal, and genetic drift, particularly with regard to genetic integrity of populations. • Population structure is thus a useful guide for a priori priority ranking with regard to genetic resource conservation , at least with regard to the extinction potential of local populations. • Geographic range alone is quite useful. The majority of species which reproduce in estuaries, river systems in the temperate zones, and in coastal pelagic zones are relatively widely distributed and fairly numerous. • Species residing in tropical floodplain rivers, extreme environments such as shallow desert lakes or salt lakes may be far less numerous and typically have rather limited geographic ranges.
  • 10. CRITERIA FOR MINIMUM POPULATION SIZES • Criteria and Time Scale • The establishment of minimum viable population sizes is one of the principal goals of conservation genetics. Other important criteria would include the demography and life history of the species, and certain ecological variables, for example, the probability and severity of catastrophe. • fishes living in shallow bodies of water in regions subject to extreme drought are likely to have a high probability of extinction. Also, they may go through severe bottlenecks with significant frequency . • At the opposite extreme, deep sea species are unlikely to be exposed to physical events which bring about a collapse in population size.
  • 11. • The “time scale of survival” is a useful device for structuring a discussion of preserving genetic variation. Somewhat arbitrarily, there are three problems or issues: 1. a short-term issue is immediate fitness – the maintenance of vigor and fecundity during an interim holding operation, usually in an artificial environment, such as when breeding domesticated or semi-domesticated fish stocks. (If, however, breeding is expected to continue for more than Ne generations, the programmed, in effect, becomes a long-term operation.) 2. the long-term issue is adaptation – the persistence of vigor and evolutionary adaptability of a population in the face of a changing environment; 3. the third issue is evolution in the broadest sense, i.e., speciation, or the creation of evolutionary novelty (Soule, 1980). For our purposes, the first and second issues are the most relevant and the third is the least relevant.
  • 12. • Survival of Captive Populations • Population Influences on Effective Population Size • The Maintenance of Long-term Fitness • Franklin (1980) argues that a minimum effective size of 500 is needed to preserve useful genetic variation, because: 1.The relevant phenotypic traits in conservation are quantitative (polygenic). For such traits the average effect of a gene is small, and most of the genetic variation is additive. 2. Weak directional or stabilizing selection does not erode additive genetic variation at a significant rate; 3. The significant evolutionary forces, therefore, are mutation, and genetic drift. That is, if a population is below some threshold size, it loses variation by drift at a faster rate than it gains variation by mutation.
  • 13. THE COMPONENTS OF GENETIC IMPOVERISHMENT IN FISH POPULATIONS Pollution Fishing pressure Sport fishing Artificial selection Reproductive isolation
  • 14. Techniques For The Conservation And Enhancement Of Genetic Resources In Closely Managed Fish Populations 1.Artificial Selection of Broodstock • Artificial selection of broodstock is broadly defined as the conscious selection of an individual or genetic group for the purpose of providing progeny for culture or stock enhancement. • This selection can be based upon the performance of an individual (individual selection), of its progeny (progeny selection), of its ancestors (pedigree selection), of its contemporary relatives or on the potential of a useful combination with a parent of another genotype (hybridization selection). • In all cases selection is practiced in order to improve the performance of the progeny group above that of a progeny group from unselected parents.
  • 15. 2.Artificial Methods of Reproduction • Methods of artificial propagation, including the use of hormones, in vitro fertilization and development, are in wide use in aquaculture. • The ways in which artificial propagation can affect the maintenance and study of genetic variation include: 1. Increase of genetic variability and genetic understanding. 2. Aids in the conservation of stocks, strains, species and other genetic groups. 3. Allows the development and use of specialized breeding methods. 4. Allows the efficient maintenance of effective population size. 5. Aids in interspecific hybridization.
  • 16. 3.Hybridization and Heterosis • Hybridization (or cross breeding) can be divided into two categories: (1) intraspecific: crosses between strains, stocks, land races, geographic populations within a species; (2) interspecific: crosses between species. • Hybridization is practiced to achieve either of two favorable outcomes. These are: • (1) heterosis or hybrid vigor, which is defined in a broad sense as an increased performance or value (to the aqua breeder) of progeny above the average of the parental performances or value, • (2) non-heterotic effects which is the performance of the progeny as the result of simple combination of parental genotypes.
  • 17. 4.Enhancement of stocks • The concept of augmentation of natural population production by introduction of hatchery raised, “cultured” juvenile fishes into natural systems. Varying levels of success have been achieved. • It is apparent that natural fish stocks undergo genetic alteration through addition and deletion of genetic material. Although quite a lot of attention has been given to effects of competition between “wild” and hatchery raised fish. • Stock enhancement through ranching is feasible only(1)if there is incomplete colonization of available habitat by juveniles and (2) if the trophic capacity of the habitat is under-utilized by a stock/its competitors. i.e. there is available carrying capacity • The successful induced spawning and larval rearing of endangered Hilsa , N chitala , H nigricollaris have opened up the avenues of ranching their advanced fingerlings in depleted water bodies for stock replenishment.
  • 18. 5 Cryopreservation of Genetic Resources • the genetic resources for (1) cultured fish stocks, (2) unique natural populations, (3) species that are threatened. At present methods for freezing fish eggs or embryos are not technically feasible but research in that area is being actively pursued (e.g., Whittingham and Rosenthal, 1978).
  • 19. 6. By using different CHROMOSOME ENGINEERING Techniques • Gynogenesis:- • Androgenesis:- • Production of diploid, triploid, tetraploid fish production:- • Production of YY stocks:- • Transgenic fish production:- • Cross breeding:-
  • 20.
  • 21. In- situ conservation Ex-situ conservation 1.The threatened species are conserved outside their natural habitats. a. Live gene bank b. Gene bank with gamete, c. Gene bank with DNA 1. Continued co-evolution where in the wild species may continue to co-evolve with other forms providing the breeders with a dynamic source of resistance that is lost in ex situ conservation 2. National parks and biosphere reserves may provide less expensive protection for the wild relatives than ex situ
  • 22. Live gene bank • In a live Gene Bank which is a Genetic Resource Centre, the endangered species are reared in captivity, bred therein and genetically managed avoiding inbreeding depression, domestication and unintended selection. The NBFGR is maintain the wild stocks of threatened species N chitala, C marulius, Tor putitora in the Mini germplasm Repository. • Gene bank with DNA:- • DNA banking which is yet to be initiated would include 1. Genomic DNA 2. DNA Library( Genomic DNA or cDNA library) 3. Cloned DNA fragments.etc
  • 23. Constraints to management and conservation of aquatic genetic resources 1. Inadequate knowledge base: • The knowledge base for managing the genetic resources of aquatic species in inadequate. Although sufficient information is available for a few intensively studied and managed species, such as salmoinds,tilapia and carp, there is paucity of even basic biological information for most of the rest. Nothing is known of their genetics. In fact, genetic research on aquatic animals has not been considered a high priority. 2. Insufficient attention 3. Magnitude of the task
  • 24. Recommendation 1.Conservation of genetic diversity must be an integral part of policies and programmers that affect aquatic animal resource development. 2. Maintenance of the genetic diversity of aquatic animal species should be considered when management and exploitation practices are developed . 3. The introduction and transfer of aquatic species should be regulated strictly by governments and should not be permitted without careful analysis of the potential ecological, biological, and genetics risks.
  • 25. Reference • Allendorf, F.W. and F.M. Utter, 1979 Population genetics. In Fish physiology, edited by W.S. Hoar, D.J. Randall and J.R. Brett. New York, Academic Press, vol.8:407–54 • Bakos, J., Z. Krasznai and T. Marian, 1978 Crossbreeding experiments with carp, tench and Asian phytophagous cyprinids. Aquacult.Hung., Szarvas, 1:51–7 • Falconer, D.S., 1960 Introduction to quantitative genetics. London, Oliver and Boyd • Frankel, O.H. and M.E. Soule, 1981 Conservation and evolution. London, Cambridge University Press • Helsop-Harrison, J., 1974 Genetic resources conservation: the end and the means. J.R.Soc.Arts, Feb.issue:157 p. • Horton, H.F. and A.C. Ott, 1976 Cryopreservation of fish spermatozoa and ova. J.Fish.Res.Board Can., 33(4) Part 2:995– 1000 • W S Lakra, A Gopalkrishnan,.2013,Genetic,Genetic Engineering and Biotechnology in Fisheries,9.cryopreservation and Fish diversity Conservation,165-171

Editor's Notes

  1. 2.A British symposium on biology and conservation of rare fish focused the attention of national and international bodies to the urgent need to give fishes a conservation status comparable to that already given to birds, mammals and other vertebrates