Current Status of Aquatic Genetic Resources Conservation and Utilization
in Thailand
Nuanmanee Pongthana
National Aquaculture
Genetics Research Institute, Department of Fisheries, Thailand
Introduction
Thailand supports an extremely diverse
aquatic fauna and flora along their supporting habitats. Situated in the Indo-Chinese and Malay
Peninsula sub-regions of the Oriental Realm, the areas of the country has been
described as a “Biogeographical Crossroad¡¨, where
comprises Indo-Burmese, Indo-Chinese and Indo-Malayan elements. Thailand’s
aquatic ecosystems are supported by two coastlines and six major river systems.
For at least 6,500 years, the economy of
the Thai people in many parts of the country has been intimately involved with
aquatic ecosystems. These
ecosystems have been important not only as a source of water but also a source
of food. In recent decades,
Thailand’s economic growth has accelerated with the
land developments, industrialization and cultivation combined with intensive
human use of freshwater and marine habitats which remained, leading to
significant threats to habitats, species and genetic diversities.
Biodiversity of aquatic resources in Thailand
Thailand extends from 50¡¦ N to 20o 30¡¦ N
and from 97o 30¡¦ E to 105o 45¡¦ E and approximately 1,500 km from north to south
and 800 km from east to west, covering 513,517 km2. The North lies between the Salween and
Mekong River systems and most of the area is drained by the headwaters of the
Chao Phraya River system. The
Northeast area drains almost entirely into the Mekong River system. The Central part has been watered by
the mainstream of the Maeklong, Chao Phaya and Bangpakong Rivers. The Maeklong system, including the Kwae
Noi and Kwae Yai, originated from the Tennasserim range of the westernmost
areas. The Peninsula Thailand
refers to the area south of 12o N latitude of southward from the Isthmus of
Kra.
The Gulf of Thailand faces to the western
part of the South China Sea to the northwest of the Indo-Malayan
Peninsula. The eastern Gulf of
Thailand has an area of 320,000 km2 and a coastline of 1,874
km. In the west is the Andaman Sea
with an area of 116,280 km2 and a coastline of 740 km.
The major inland resources available for
freshwater aquaculture and fisheries comprises 66 rivers, 10,233 lakes and
swamps, 685 reservoirs and man-made lakes with the total water surface of
566,400 hectares. The six major
river drainages are: the Salween, Mekong, rivers of southern Peninsula,
southeastern part, Chao Phraya and Maeklong River systems.
The Salween River originates in the
Tibethan range of the eastern Himalayas, and covers 324,000 km2 of
the drainage area. The river
drainages pass through western Yunnan, China, and passes the Thai-Myanmar
border and then runs off to the Andaman Sea at Martaban Bay. The Salween River system supports a
unique Indo-Burmese fauna which is different from the other river systems in
the country, but share similarities with the Ganges and Irrawaddi River
faunas. At least 29 species are
exclusively found in the river, (endemic), including cyprinids (Rohtee alfrediana, Aspidoparia morrah, Hampala
salweenensis); catfishes (Aoriithys
seenghala, Hemibagrus microphthalmus,
Gagata sp., Exostoma vinciguerri, Pseudoechenius
sulcatus); spiny eels (Mastacembelus
alboguttatus); glassperch (Parambassis
wollmeri) etc.
The Maeklong River system includes the
Petchburi River and other drainages above the Ishmus of Kra, the Rivers
originated from the eastern side of Tennaserim Range and runs off to the Gulf
of Thailand. The watersheds have
been supported by the vast areas of the western rain forest. Over 144 fish species were found.
Peninsula Thailand supports Indo-Malayan
fauna and flora, with affinities toward the south. The area commences southward of the Ishmus of Kra, extending
throughout the Malay Peninsula.
The two mountains ranges of the southern Tennaserim and Khao Bantad,
which receive Thailand’s highest rainfall, are the backbone of
the Peninsula. The Khao Bantad
Range supports the most extensive river systems. Six main but short river systems drain the Peninsula, three
Rivers runs off to the Gulf of Thailand, and two Rivers drain to the Andaman
Sea. Over 140 fish species were
found.
Rivers of the southeast Thailand covers
less extensive area of the southeastern part of the country, drained by
relatively short mainstreams of three rivers. This is one of least seasonal area in Thailand, similar to
the Peninsula both in the aspect of climatic and species occurrence. At least 120 freshwater fishes occurs,
four species are exclusive to the area; Koh Chang Loach Schistura kochangensis, Myers’s
Loach Pangio myersi, cyprinid Oreiichthys parvus and Mouth-brooder
Betta Betta prima. More examples of affinity to the
Peninsula are Asian Bony-tongue Scleropages
formosus, Dwarf Rasbora Boraras
maculata and Torrent stream Catfish Pterocryptis
torrentis.
The Chao Phraya River system is the main
blood vessels of the northern and central continental Thailand, originated from
watersheds of the two mountains ranges.
The system has been drained into by four major rivers; Ping, Wang, Yom
and Nan Rivers, conjuncted into mainstream of Chao Phraya River at
Nakonsawan. The River connects
with three tributaries; Sakaekrung and Tachin from western, Pasak from the
Petchabun Range, northeastern and Bangpakong from the Bantad Range, southeastern,
then the system runs off to the Gulf of Thailand.
So far, 250 species of fishes are known
but two catfishes thought to be endemic species, schilbeid Platytropius siamensis and mountain-stream sisorid Oreoglanis siamensis, both considered as
a risk while the former species is thought to be on the brink of
extinction. The Banpakong River,
eastern tributary is an important habitat of the relict stock of the Chao
Phraya fish species, whereas several species which disappeared from the
mainstream i.e. Albulichthys albuloides,
Macrochiricthys macrochirus, Cyclocheilicthys heteronema still rarely
occur in this River.
The Mekong River is ranked as the 11th
longest world’s rivers. Originated from the eastern Tibethan Plateau, drained
through six countries; China, Myanmar, Laos PDR, Thailand, Kampuchea, along
4,200 km, then runs off to the South China Sea at the Mekong Delta of southern
Vietnam. Over half of the River
length has drained through Thailand consists ca. 77% of the entire basin area. There are three main tributaries; the
Chi-Mun Rivers of Northeast Thailand, the Nam Nguem and Nam Teun Rivers of Laos
PDR and the Tonle Sap River of Kampuchea where connected with the Grand Lake.
The Mekong River system is inhabited by
over 1000 species of fish. In the Thai
portion, the River possesses at least 289 species. Some Chinese species affinity may occur, i.e. mud gudgean Abbottina rivularis, loach Sinibotia longiventralis and bagrid
catfish Mystus pleuriradiatus. Over 30 fish species are endemic to
this river, ranges from the largest Giant Catfish Pangasianodon gigas of the mainstream, to the 3rd
smallest cyprinid Boraras micros of
the marshland.
The recent checklist reported at least 17
orders, 56 families and 570 species of freshwater fishes occur to Thailand, the
largest family is Cyprinidae, possesses 204 species. The second is Balitoridae, 62 species known and Cobitidae,
31 species respectively. The River
system which supports largest species number of the country is the Chao Phraya
River, from which 329 species known.
The Mekong basin of Thailand possesses 290 species; at least 270 fish
species found in the Peninsula Thailand; the Maeklong basin possesses at least
207 species; the Southeast Thailand is found 166 species. The least species number is reported
from the Salween basin of the country of 111 species. Additionally 15 introduced or exotic freshwater fish species
was populated or flourished in natural waters (Table 1).
Aquatic resources utilization in Thailand
In Thailand, capture fishery accounts for
the bulk or 52% of the total production, while the rest or 48% production comes
from aquaculture. Marine fisheries
accounts for 94% of the total capture fishery, while coastal aquaculture
accounts for 79% of the total aquaculture production. Coastal aquaculture covers the production areas of 749.416
km2, while freshwater culture covers the production areas of 583.992
km2. The total fish
production in 1995 was 3.5726 million tons with a total value of US$ 2,402.79 million. Part of the production is for domestic
consumption, the rest is for export.
In 1995, the exported quantity was 1,192,560 tons with a total exported
value of US$ 29.14445 million.
Importance of aquatic genetic resource
conservation to Thailand
The need for genetically improved
aquaculture broodstock in Thailand is now widely recognized as natural
populations of aquatic animals are fished out nearly to the point of
extinction, and aquaculture supplies an increasing proportion of the food
protein requirements of rural peoples.
The value of genetic conservation in aquaculture has been recognized
more recently.
Due to the conservation strategy for any
aquatic species depends on its biology, genetic diversity within and between
different populations and stresses that are modifying each population. One of the impediment to conservation
of fish germplasm resources of Thailand is the lack of database on the above
aspects. Genetic information is
inadequate and biological information from different geographic populations of
each species is limited.
Due to the high demand of large
population and the rapidly developing aquaculture industry, aquatic
biodiversity in Thailand is under a very high stress. Loss of biodiversity throughout Thailand may severely limit
the sustainable development of aquaculture and fisheries. Genetic conservation of aquatic
organisms becomes a critical problem for the sustainable development of
aquaculture industry. Some efforts
have been made by the government and fisheries scientists, but not much.
Impacts of hatchery stocks on wild fish
has been realized. Due to hatchery
breeding and rearing practices, the genetic variation and life history traits
of farmed fishes differ considerably from wild fish. Broodstocks maintained for hatchery operations are subject
to artificial selection for production traits or unintended selection at the
time of establishing founder stocks or during domestication. Selection for specific traits generally
result in reduced genetic variance and fitness. Due to massive introduction of cultured fish, displacement
of wild stocks may be found and high levels of introgression of the altered
hatchery fish genome into wild stocks may be taken place and may have serious
implications for long term survival of wild stocks. Escape of farmed fish and inter breeding with wild
populations can result in decreased fitness of wild stocks.
In Thailand, specific studies to show the
genetic consequences of hatchery stocks on wild fish is lacking. Due to the ongoing programs of the
Department of Fisheries for stocking reservoirs and rivers with hatchery bred
seed of various fish species, the level of introgression is different between
hatcheries may threaten the genetic purity and variability of wild stocks. Also, by stocking natural waters with
hatchery seed from broodstock originating from a different geographic area,
there is danger of homogenization of natural genetic diversity. The immediate requirement is to develop
a breeding strategy that can be easily applied in commercial hatcheries to
avoid inadvertent selection, inbreeding and introgression. Seed for ranching operations should be
derived from wild stocks of that particular geographic area to avoid dilution
of natural genetic.
In conclusion, most of the conservation
efforts in Thailand are targeted at the level of ecosystem or species. Based on the genetic variation within
and between populations, a species has the capacity to adopt to varying
environmental conditions. Also the
genetic variability within a species forms the foundation on which genetic
upgradation programs can be based.
Therefore, there is urgent need to take effective steps to safeguard
against negative genetic consequences of escaped farmed fish.
Status of aquatic genetic resource conservation
and utilization in Thailand
Conservation of aquatic genetic resources
that prevent the deterioration of environments and regulate harvesting,
culturing and transfers and introductions has recently become a national
priority to avert the loss of many important aquatic species.
Thailand’s
current and future aquatic genetic resources activities comprise the following:
¡PCharacterization
and evaluation of aquatic genetic resources.
¡P Baseline information, performance
recording and molecular characterization in many cultured aquatic species, i.e.
carp species, marine shrimp, oysters, catfishes, freshwater prawn, etc.
¡PConservation/utilization
of aquatic genetic resources, with sustainable use.
¡P In situ conservation via restrictions on fishing gear, times and season
for the marine and freshwater resources.
¡P Ex situ conservation via developing
of cryopreservation protocols in many cultured aquatic species, i.e. catfishes,
carps, marine fishes, etc. as well as in genetically improved breeds of Silver
barb and catfish for further dissemination
¡P germplasm transfers of genetically
improved tilapia and common carp.
¡P
Development of the national database on the diversity
of aquatic species.
¡P
A member of an International Network on Genetics in
Aquaculture (INGA).
¡P Management of enhanced fisheries and
aquaculture.
¡P Policy of property rights, national
legislation/control on aquatic genetic resources.
Table 1. List of introduced or exotic freshwater fishes available in
Thailand.
Species list |
Year introduced |
Introduced from |
Origin |
Family
Cyprinidae |
|
|
|
Cyprinus
carpio Linnaeus, 1758 |
1912 |
China |
China |
Carassius
auratus Linnaeus, 1758 |
1980 |
Japan |
China |
Ctenopharyngodon
idellus Valenciennes, 1842 |
1922 |
China |
China |
Hypophthalmicthys
molitrix Valenciennes, 1844 |
1932 |
China |
China |
Hypophthalmicthys
nobilis Richardson 1844 |
1922 |
China |
China |
Labeo
rohita Hamilton 1822 |
1968 |
India |
Ganges basin |
Cirrhina
mrigla Hamilton 1822 |
1980 |
Bangladesh |
Ganges basin |
Family
Characidae |
|
|
|
Colossoma
bidens Spix 1829 |
1980 |
Hongkong |
Amazonia |
Family
Ictaluridae |
|
|
|
Ictalurus
punctatus Rafinesque 1818 |
1981 |
USA |
USA |
Family
Clariidae |
|
|
|
Clarias
gareipinus Burchell 1822 |
1985 |
Laos PDR |
Africa |
Family
Loricaridae |
|
|
|
Hypostomus
plecostomus Linnaeus 1758 |
1977 |
Hongkong |
Amazonia |
Family
Cichidae |
|
|
|
Oreochromis
mossambicus Peters 1852 |
1948 |
Malaysia |
Africa |
Oreochromis
niloticus Linnaeus 1758 |
1965 |
Japan |
Nile basin |
Oreochromis
aureus Steindachner 1864 |
1957 |
Belgium |
Africa |
Family
Poecilidae |
|
|
|
Poecilia
reticulata Peters 1859 |
1947 |
Singapore |
Central America |
Gambusia
affinis Baird and Girald 1853 |
1947 |
Belgium |
Central America |