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Conservation and Utilization of Farm
Animal and Aquatic Genetic Resources in Chinese Taipei:Part I. Farm Animals
Hsiu-Luan Chang, Chinese Taipei
There has been an increasing awareness in
the importance of the conservation of animal genetic resources, not only of
wildlife, but also of domestic livestock since the early of 1960s. For the global survey data with pig,
cattle, buffalo, goat, sheep, horse and ass obtained by FAO, there are 2,719
breeds currently utilized and over 390 breeds of those are known to be at risk
(Loftus, 1994). Most of indigenous
breeds in Chinese Taipei, which were important for animal industry due to their
local favorite, are subject to elimination for low production efficiency when
compared to that of exotic breeds, although native chicken and Tsaiya duck are
still utilized in the domestic commercial level not international market. The native breeds generally maintain
one or more adapting characteristics to the living environment, which may
provide useful or potentially useful genes or combinations of genes for the
future needs. For example,
prolificacy and early maturity of pig, heat tolerance of Taiwan yellow cattle,
disease-resistance of Formosan buffalo, roughage tolerance of Chinese goose and
meat flavor of native chicken.
Furthermore, most of native breeds in Chinese Taipei are still raised in
graze product system. This was
recognized at the 8th Board Meeting of the Advisors for Science and
Technology-Agriculture
Group in Chinese Taipei in April 1986, which formally recommended that life
resources should be preserved so that their genes will not be forever lost due
to the concentration on a limited and highly selected strains. Consequently a large-scale pilot
national project, “Germplasm Preservation and Utilization in Domestic Animals”,
was initiated in 1987.
Objectives
Taiwan Livestock Research Institute (TLRI)
along with its branch institutes and propagation stations, together with Animal
Science Departments in both National Taiwan University and National Chung-Hsing
University, were selected as primary sites to conserve and propagate living
population for native farm animals.
The main objectives of the conservation programme are:
1. to
establish native farm animal populations for conservation of animal genetic
resources and to prevent genetic erosion.
2. to
collect informative data on physiology, genetic and economic related traits as
well as living habit for characterization of native breeds which may provide
valuable genetic resources in developing alternative stocks with
characteristics of native breeds for meeting a wide variety of
market/production conditions.
3. to establish a
multi-faceted, computerized information and communication system to support the
descriptive information, e.g., performance and production attributes of farm
animals.
4. to apply biotechniques
in conservation of germ cells for conserved native breeding stocks and thus
corresponding genetic materials.
The action plan calls for amalgamation of
existing capabilities of all animal research related units with the TLRI
playing a nuclear role. In the
program, the COA is the highest authority in setting guidelines and in
providing funds for operations and research projects. On the operational aspects, the Department of Agriculture
and Forestry under the Taiwan Provincial Government (PDAF) directs its
subordinate research institutes and stations to implement the conservation
activities.
Methods for Conservation and Utilization
There are three methods have been used to
preserve livestock germplasm, i.e., maintaining live populations,
cryopreserving germ cells, and establishing DNA stores. Animal resources in Chinese Taipei are
bounteous and are preserved for improving exotic breeds in terms of future
production performance and efficiency.
Conservation and integration of germplasm for new variants are attempts
to use the gene pool adequately in Chinese Taipei. Protocols on conserving livestock germplasm in Chinese
Taipei are as follows:
-standards
set up for visible characteristics of conserved breeds
-collection
of native animals from small farmers
-selection
of the place of conservation
-propagation
using a small population at random; if animals have economic traits for
improving production performance of exotic breeds, the intercrossing program is
used
-data
collection on their growth, reproduction, living habits, and genetic
polymorphism
-preservation
of germ cells with emphasis at sperm and embryo cryopreservation
-information
exchange and providing for public needs
-typical
animals after propagation with benefits of cooperative germplasm research are
released to the private sector
-promotion
of public extension and education with intellectual property rights for this
germplasm relative to arts and culture
-sharing
the world’s genetic diversity and turning potential into reality
Progress
and Current Status
In Chinese Taipei, conservation of genetic
resources is achieved by maintaining live breeding stocks or cryopreserved
semen, ova, eggs and embryos as well as DNA.
1. Maintaining
Live Populations:
With financial support
from the government, small living populations of native farm animals are conserved
in TLRI and experimental farms of universities. Also, the Jomalie Farm of the Farmers’ Cooperation at Tainan
County keep some of the native breeds and are financially supported by the
public, who pay to enter. Breeds
and number of animals maintained at conservation locations in 1998 are shown in
Table 1. Numbers of breeding
stocks in conserved populations and associated effective population sizes as
well as estimated inbreeding coefficients are in Table 2. Results based from survey data conducted in
August 1993 and July 1998, respectively, were shown in Table 3, which indicated
the total number of native farm animals conserved by conservation farms were
about 1.1% and 4.0%of those raised by private
farmers in the corresponding years.
However, both total numbers of the animals preserved in private and
conservation farms are decreased in 1998, which account for around 15.0% and
59.4% of livestock conserved at private and conservation farms, respectively,
in 1993. Conservation per se is not a priority unless there is
some economic benefit associated with such actions. The power of the market place indicates that genetic
conservation at the private sector level will be successful only if incentives
for producers exist. Native breeds
in Chinese Taipei are usually being maintained as a hedge
for potential shifts in market demands.
However, these livestock will be subject to elimination if there seems
to be no perceived economic advantage for the animals in a short period of
time.
2. Cryopreservation
of genetic resources:
Cryopreservation of semen,
ova, eggs and embryos as well as DNA from native breeds was conducted to
preserve the variance of genetic resources in Chinese Taipei, because of the
limitations of animal-raising facilities and financial support. The quantity of Thus the freezing
techniques for semen of yellow cattle, black goat, pigs, native chicken, Tsaiya
ducks, and Chinese geese were developed and applied in field tests to check the
survivability of thawed sperm.
Embryos of yellow cattle, black goat, Lanyu pig, and Taoyuan pig were
frozen in liquid nitrogen. Embryo
mortality was tested after thawing by transfer into surrogate mothers. This met with no success in several
trials. But when fresh embryos
were transferred directly, nine Lanyu piglets and one Taiwan Black goat kid
were born alive in 1991.
3. Identification
of genotypes:
In order to establish a molecular-based
data bank for animal genetic resources monitoring and exchanging, blood typing
was conducted for conserved animals.
Results obtained from GPI (glucose phosphate isomerase) and PGD
(phosphogluconate dehydrogenase) test indicated that most of individuals
conserved in population were homozygous.
Mitochondrial DNA (mtDNA) is maternally inherited by random segregation
through the egg cytoplasm and can be used to trace back their maternal
genealogy. It is also thought to
be one potential source of genetic variation for phenotypic characteristics of
animals. The polymorphism of mtDNA
among some of the native and exotic livestock breeds in Chinese Taipei were
analyzed. The cleavage patterns of
Hind III, EcoR V, and Bgl II are listed in Table 5. For further use in germplasm conservation, a detail sequence
and organization of mtDNA should be carried out. It should be related to their maternal characteristics in
order to trace back their origin.
4. Documentation
and related publications entitled as follows:
(1)“Handbook of Germplasm Preservation and Utilization in Animal Science-Taiwan” published in 1990.
(2)“Catalogue of the Native Poultry of Southeast Asia” published in 1991.
(3)“Genetic Resources Information of Native Livestock and Poultry Breeds
in Taiwan” published in 1992.
(4)“Conservation and Genetic Relevance of Domestic Livestock and Poultry
in Taiwan” published in 1993.
(5)“Genetic Lineage of Conserved
Livestock and Poultry in Taiwan” published in 1996.
5. Communication
and exchanging information:
Mass
communication of genetic resources information for native breeds is one of the
main tasks in the nation-wide project.
It can provide bilateral information exchange between public and private
initiatives of animal genetic resources conservation, and thus benefit to
economic, scientific, and sociocultural aspects. Therefore, both videotapes and compact disc were produced
for public as requested.
Information network was set up to provide timely information for global
user.
(1) A series of six videotapes with “Animal
Fire” entitled was produced in 1993, which aimed to introduce the cultural and
artistic roles of pig, cattle, goat, chicken, duck and goose in the China
humanities, therefore, the social values on this aspect would be enlarged in
public. In addition to Chinese
version, Taiwanese, Guochia (one of dialects in China), English and Japanese as
well as Spanish versions are currently available for requested.
(2) Scientific videotape series(including both “Native Livestock”
and “Native Poultry” parts)entitled “Germplasm Utilization Series-Animal Conservation” produced in 1994.
(3) Compact disc entitled “Motion Information on Germplasm of Domestic Animals:Taiwan Breeds” produced in 1994.
(4) The
Bulletin Board Station (BBS) with IP address being cc.tlri.gov.tw was
initiated in 1995 to provide bilateral communication site on germplasm related
information for all interested individuals and organizations.
(5) In
1997, a Home Page on Internet provides timely and detailed information on
inventories of native farm animal genetic resources and conservation issues so
that user world-wide can obtain up-to-date information. This can be accessed at URL: http://www.angrin.tlri.gov.tw
Future Objectives and Potential Action
Plans:
The major objectives in the near
future are:
1. to
establish a molecular-based data bank for animal genetic diversity monitoring
and exchanging,
2. to strengthen human resource development
and promote the efficiency of information exchange in animal genetic resources.
In
order to attain the above goals, the following action plans are proposed:
1. Establishment
of the Genetic Resources Information Network Stations (GRINS): An information
network of county-based should be developed for users across the country. Also, national programs for surveying
and monitoring population size of animals as well as reducing the loss of
domestic diversity are essential for the utilization of native domestic
animals.
2. Strengthening of science and technology
training: More emphasis should be given to training programs relevant to the
science and technology in germplasm preservation and utilization as well as the
identification of genetic variation.
Human resource could thus be developed, and hence the establishment of
genebank could be accomplished.
3. Establishment of cryopreservation
facilities for animal germ cells: The freezing techniques can be applied to
preserve eggs, sperms and embryos, which might be, used both for genetic
characteristic study and animal diversity analysis. In addition, the DNA preservation technique can be also used
for germplasm conservation.
Table 1. Native
breeds and population size maintained at conservation locations in 1998
Location
|
Breeds
|
Male
|
Female
|
TLRI1 headquarters
|
Taoyuan pig
|
38
|
63
|
TLRI Ilan Branch Institute
|
Brown Tsaiya duck
|
34
|
108
|
|
White Tsaiya duck
|
38
|
118
|
|
Black Muscovy duck
|
38
|
114
|
TLRI Hualien BAPS2
|
Formosan buffalo
|
19
|
61
|
|
Formosan goat
|
22
|
103
|
TLRI Changhwa BAPS
|
Brown Chinese
goose
|
26
|
78
|
|
White Chinese
goose
|
21
|
77
|
TLRI Taitung BAPS
|
Lanyu pig
|
47
|
72
|
TLRI Kaohsiung BAPS
|
Formosan Sika
deer
|
12
|
25
|
|
Formosan Sambar
deer
|
28
|
19
|
TLRI Hengchung Branch Institute
|
Taiwan Yellow
cattle
|
43
|
166
|
|
Formosan goat
|
50
|
131
|
Natl. Taiwan Univ.
|
Lee-Sung pig
|
34
|
50
|
Natl. Chung-Hsing
Univ.
|
Native chicken
|
103
|
252
|
1TLRI=Taiwan Livestock Research
Institute
2BAPS=Breeding Animal Propagation
Station
Table 2. Numbers of native breeding stocks conserved and associated effective
population sizes and estimated inbreeding coefficients in 1998
Breed
|
Breeding
stocks
|
Effective population size
|
Inbreeding coefficient
(Estimated, %)
|
Male
|
Female
|
Taoyuan pig
|
10
|
35
|
31.1
|
1.61
|
Lanyu pig
|
9
|
35
|
28.6
|
1.75
|
Lee-Sung pig
|
10
|
20
|
26.7
|
1.88
|
Formosan buffalo
|
3
|
42
|
11.2
|
4.46
|
Taiwan Yellow cattle
|
16
|
108
|
55.7
|
0.90
|
Formosan goat(1)
|
3
|
50
|
11.3
|
4.42
|
Formosan goat(2)
|
7
|
55
|
24.8
|
2.01
|
Formosan Sika Deer
|
9
|
11
|
19.8
|
2.53
|
Formosan Sambar Deer
|
18
|
10
|
25.7
|
1.94
|
Native chicken
|
128
|
265
|
-
|
-
|
Brown Tsaiya duck
|
34
|
108
|
103.4
|
0.48
|
White Tsaiya duck
|
38
|
118
|
115.0
|
0.43
|
Black Muscovy duck
|
38
|
114
|
114.0
|
0.44
|
Brown Chinese goose
|
7
|
27
|
22.2
|
2.25
|
White Chinese goose
|
5
|
25
|
16.7
|
3.00
|
(1)Animals conserved at TLRI
Hualien BAPS
(2)Animals conserved at TLRI Hengchung
Branch Institute
Table 3. Numbers of native breeding stocks in Chinese Taipei
Breed
|
Private farm
|
|
|
Conservation farm
|
Male
|
|
Female
|
|
|
Male
|
|
Female
|
1993
|
1998
|
|
1993
|
1998
|
1993
|
1998
|
1993
|
1998
|
Pig
|
|
|
|
|
|
Taoyuan pig
|
22
|
35
|
1678
|
2734
|
10
|
10
|
30
|
35
|
Lanyu pig
|
67
|
68
|
126
|
138
|
15
|
9
|
45
|
35
|
Lee-Sung pig
|
0
|
0
|
0
|
0
|
15
|
10
|
30
|
20
|
Cattle
|
|
|
|
|
|
Formosan buffalo
|
166
|
212
|
997
|
820
|
2
|
3
|
30
|
42
|
Taiwan yellow
|
1540
|
145
|
1925
|
222
|
11
|
16
|
70
|
108
|
Goat
|
|
|
|
|
|
|
|
|
Formosan goat
|
1051
|
108
|
4045
|
877
|
9
|
10
|
90
|
105
|
Deer
|
|
|
|
|
|
|
|
|
Formosan Sika
|
990
|
355
|
919
|
523
|
16
|
9
|
25
|
11
|
Formosan Sambar
|
1193
|
921
|
1049
|
951
|
9
|
18
|
13
|
10
|
Chicken
|
|
|
|
|
|
Single comb
|
1944
|
1218
|
53579
|
2719
|
200
|
88
|
800
|
180
|
Pea comb
|
3110
|
716
|
72721
|
2037
|
35
|
40
|
100
|
85
|
Duck
|
|
|
|
|
|
Brown Tsaiya
|
1506
|
206
|
34115
|
3073
|
80
|
34
|
200
|
108
|
Black Muscovy
|
2165
|
460
|
9413
|
1863
|
70
|
38
|
70
|
114
|
Goose
|
|
|
|
|
|
Brown Chinese
|
398
|
788
|
1185
|
2478
|
40
|
7
|
120
|
27
|
White Chinese
|
611
|
1328
|
3976
|
4992
|
40
|
5
|
120
|
25
|
Total
|
14763
|
6560
|
185728
|
23427
|
552
|
297
|
1743
|
905
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Table
4. Cryopreservation of genetic resources for native breeds in Chinese Taipei
Breed
|
Semen
|
Ova
|
Embryo
|
Egg
|
DNA
|
Taoyuan pig
|
0
|
0
|
0
|
-
|
63
|
Lanyu pig
|
0
|
30
|
30
|
-
|
78
|
Lee-Sung pig
|
0
|
0
|
0
|
-
|
63
|
Formosan buffalo
|
400
|
0
|
0
|
-
|
61
|
Taiwan yellow cattle
|
122
|
0
|
43
|
-
|
110
|
Formosan goat
|
1530
|
87
|
0
|
-
|
12
|
Formosan Sambar deer
|
0
|
0
|
0
|
-
|
5
|
Native chicken
|
0
|
0
|
0
|
0
|
67
|
Brown Tsaiya duck
|
0
|
0
|
0
|
160
|
16
|
Black Muscovy duck
|
0
|
0
|
0
|
100
|
7
|
Brown Chinese goose
|
0
|
0
|
0
|
0
|
103
|
White Chinese goose
|
0
|
0
|
0
|
0
|
102
|
Table 5. Mitochondrial DNA
fragments of several native and exotic breeds in Chinese Taipei
Breed
|
Number of fragments
|
Size of mtDNA estimated (kb)
|
Hind III
|
EcoR V
|
Bgl II
|
Taoyuan
or Yorkshire pig
|
4
|
1
|
1
|
16.35
|
Lanyu
pig
|
4
|
1
|
2
|
16.35
|
Landrace
or Duroc pig
|
4
|
1
|
3
|
16.35
|
Formosan
buffalo
|
3
|
1
|
0
|
16.80
|
Formosan
goat
|
3
|
1
|
3
|
16.40
|
Barbados
Black-belly sheep
|
1
|
1
|
1
|
16.40
|
New Zealand
White rabbit
|
7
|
1
|
2
|
17.20
|
Rex
rabbit
|
7
|
1
|
2
|
17.20
|
Brown
Tsaiya duck
|
4
|
-
|
0
|
16.60
|
Conservation and Utilization of Farm
Animal and Aquatic Genetic Resources in Chinese Taipei:Part II. Aquatic Organisms
Chung-Zen Shyu,
Chinese Taipei
Chinese Taipei, as an island country
surrounded by subtropical ocean, is abundant in marine organisms. There are
also abundant freshwater species. A landlocked salmon species, Oncorhynchus masou formosanus, is
especially well-known. On the other hand, aquacultural technologies in Chinese
Taipei are advanced. Many exotic species are introduced from all over the
world. However, owing to overfishing, illegal fishing by chemicals and
explosives, pollution of the sea and rivers, deterioration of inhabitants and
invasion of exotic species, resources of indigenous aquatic organisms are
depleted. Some are even reach distinction. Works of conservation and recovery
are urgently in need. It is only when the species and population are surveyed, collected,
identified, protected, and the gcrtnplasm banks for aquatic organism are
established, conservation and recovery are possible.
For the purpose of establishing germplasm
bank for aquatic organism, a project, funded by Council of Agriculture, was conducted
for investigating the genetic resources of aquatic organism in Chinese Taipei
by Academia Sinica, National Taiwan University, National Taiwan Ocean
University and Taiwan Fisheries Research Institute. The project includes
freshwater and seawater organisms, that are served as germplasm in Chinese
Taipei, such as finfish, crustacea, macroalgae, microalgae. The results of the
survey showed that most of the conservation of genetic resources are of ex situ
conservation of finfish broodstock, microalgae as feed and cryoperservation of
sperms, by private farm or public institution for aquaculture purpose. A few
microalgae species are conserved of research on toxicology or marine ecology.
Several cases of in situ conservation are practiced such as land-lock salmon
and their habitates in upstream' of central Taiwan, coral reefs and aquatic
organisms in Kenting National Park in southern Taiwan, etc.
However,
governmental policy and institution for conservation of genetic resources of
aquatic organism so far is not well established. Researches are scattered. A
centralized germplasm bank is needed for a subtropical area like Chinese
Taipei, with great diversity of aquatic species for the purpose of conservation
and aquacultural application. A project for founding a national aquatic
germplasm bank in Taiwan Fisheries Research Institute was well planned and will
soon be under construction. It is hoped that this germplasm bank will not only
play the role as central institution for conservation and utilization of genetic
resources of aquatic organism in Chinese Taipei, but also serve as windows for
international exchange of information and germplasm of aquatic organisms for
mutual benefit.
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