Marine Fish Culture in Vietnam

 

Dao Manh Son[1]

 

Abstract

Vietnam has natural conditions favourable for marine fish culture with a 3,260-km coastline and a large exclusive economic zone of about 1,000,000 km2.  Marine fish culture in Vietnam commenced in the 1960s, however during the subsequent 30 years, development has been slow.  Since 1990, commercial floating net-cage, pen and cage culture has expanded considerably with an annual production of 30,000 tonnes.  In recent years, considerable efforts have been made to develop marine fish culture of grouper, snapper, yellowtail, seabream, black kingfish, and wrasse.  Marketable size fish and fry are sold live to China, Hong Kong or Japan by boat.  Last year, more than 130 tonnes of grouper, snapper and seabream, and 450,000 yellowtail fry were exported.  Studies on the technology of grow out culture and artificial breeding of some marine fish species are also carried out.  Some experiments on artificial seed production of grouper, snapper and black kingfish were successful, though survival rate is still very low.  Despite marine fish culture having good potential for development, there are various constraints to overcome.

 

Introduction

Vietnam has a coastline of 3,260 km, a large exclusive economic zone (EEZ) of about 1,000,000km2 and more than 4,000 islands.  These natural conditions are favourable for mariculture, especially for marine fish, mollusc, and seaweed farming.  Marine fish culture in Vietnam commenced in the 1960s with species such as mullet, milkfish, and seabass.  However, during the subsequent 30 years, development has been slow.  Since 1990, commercial floating net-cage, pen and cage culture has improved considerably with an annual production of 30,000 tonnes.  In recent years, considerable efforts have been made to develop marine fish culture of grouper, snapper, yellowtail, seabream and black kingfish.  Some initial successes have been achieved in creating a new aquaculture industry, but certain constraints still remain.

Overview of marine fish aquaculture in Vietnam

Along coast of Vietnam, there are many species that can be used for mariculture.  The main species for floating net-cage culture are grouper, snapper, seabream, yellowtail, kingfish, and wrasse.  In pond, lagoon and pen culture, the main species are seabass, milkfish, mullet, and Tilapia.  The most highly valued species for culture are the groupers; the most common species greasy grouper (Epinephelus tauvina), E. bleekeri, E. areolatus, E. awoara, E. moara, red-spotted grouper (E. akaara), E. fasciatus, E. fuscoguttatus, E. malabaricus and humpback grouper (Cromileptes altivelis). 

Among them the red-spotted grouper (E. akaara) and E. bleekeri command the highest price, although other grouper species also have valuable potential markets.  All 23 species of grouper found in Vietnamese water are collected for export.

The production of marine fish culture at present in Vietnam is very low.  Every year, it is estimated that more than 130 tonnes of grouper, snapper, seabream and other minor fish and 500,000 yellowtail fry are exported.  Separate statistics for species are not available.  The total number of cages and production of marine fish culture in 1995 is shown in Table 1.

Table 1.  Number of cages and production of fish mariculture in Vietnam.

Province

Number of cages

Estimated production (tonnes)

Quang Ninh

126

40.0

Hai Phong

130

 

30.0

Thua Thien - Hue

120 (bamboo cage)

8.0

Da Nang

130

5.0

(450,000 yellowtail)

Nha Trang

60 (stationary cage)

25.0

Binh Thuan - Kien Giang

70

15.0

Total

636 cages

123.0

The two main types of marine fish culture practised in Vietnam are fry/fish holding and fry/fish growing.  The former is the main type of production throughout the country.  Marketable-sized fish or fry are bought from fishermen, who use hooks, long line, traps, purse seines or trawls.  The fish are then kept for between one week and two months before being sold live to middleman or Hong Kong buyers.  Only three provinces (Quang Ninh, Thua Thien-Hue and Nha Trang) have some facilities for grow-out culture, but the culture techniques are very simple.  In these areas, fingerlings of 10-18 cm are stocked at about 50-60 pieces/m3.  Trash fish are used for feed at about 5-10% of body weight per day.  Cages are of simple design with a frame system made of hard wood planks either tied or bolted together, and kept afloat by simple 200 litre plastic drums or styrofoam covered by a woven plastic cloth.  The single cage units are 2x2x2m3, 3x3x3m3 or 4.5x4.5x4.5m3 and are made of knotless netting.  Bamboo cages are used in Thua Thien-Hue.

Of the approximately 3,260 km coastal region, at least 1,200 km is estimated as suitable for cage farming of marine fish species.  The most suitable areas are Ha Long Bay at Quang Ninh, around Cat Ba Island at Hai Phong, Tam Giang-Cau Hai lagoon at Thua Thien-Hue, Son Tra peninsula at Da Nang, and in Cam Ranh and Nha Trang bays.

The marketing channels for aquaculture products are varied.  The majority of live fish and fry are transported by boat to China, Hong Kong and to Japan (in the case of yellowtail).  The prices for different grouper species of live fish at marketable- sized (400-1500g) range from US$8 to US$18 per kg.  The prices for live seabass and snapper with the size of 1 to 3 kg ranges from US$5 to 7 per kg.  The prices for frozen fillets of seabass and grouper are US$8 to 10 per kg, for red snapper and red seabream are US$3.5 and US$7 per kg, respectively.  The prices of grouper fry range from US$0.3 to 2 per piece depending on size and season.  Groupers are considered the species with the most potential for marine aquaculture in the region, because the species is highly valued and has a large potential market.

Coral reefs and associated fisheries

Coral reefs in Vietnam are mainly found south of the Quy Nhon in the form of near-shore coral reefs, and as larger and deeper offshore reefs around the Hoang Sa (Paracel), Truong Sa (Spratly) and Son Tu Tay in the Spratly islands.  According to Yet (1994), there are 76 genera and over 298 species of corals, some of which are threatened.  Extensive areas of coral around Cat Ba island have been degraded by siltation caused by watershed changes, and most near-shore corals are thought to be heavily exploited for various purposes including coral mining for lime and fishing, in some cases using dynamite and other destructive fishing method.

Corals also provide inputs to certain aquaculture system, particularly lobster (as around Nha Trang) and marine fish cage culture.  Degraded reefs may be suitable for culture of Eucheuma seaweed, as is practised in some other countries of the region.  According to available data, there are about 123 genera and 327 coral reef fish species in the Spratly islands area.  The main species are wrasses (17.98%), butterflyfishes (7.92%), groupers and snappers (5.48%), soldierfishes (4.26%), moray eels (2.35%), pipefishes and other species.  Coral reef fish resources are exploited mainly as food fish.  Ornamental and aquarium fishes are hunted at a low level, so the resources are still very abundant.  Until now, no detailed data on coral reef fisheries are available.

Aquaculture system and management

Although there are more than 450 fish hatcheries in Vietnam, all are for freshwater species.  For marine fish culture, almost all fry are collected from the wild.  The availability of fry varies greatly from year to year making it difficult or impossible for farmers to fully utilise their cages.

Northern region (from Quang Ninh to Ha Tinh)

In Hai Phong and Quang Ninh provinces, the marine fish farming industry started in 1989.  The highest annual catch of 500,000 fry was in 1991.  The mean annual catch is estimated at 300,000 pieces.  Groupers comprise about half of the catch, with the rest split between seabream, snapper (20%), seabass, and Bostrichthys sinensis (30%).  In 1992, 300,000 red seabream fry were caught in the northern Ha Long Bay, but the next year only 7,000 pieces were caught.  The fry catching period is from March to July (main season in April and May).  In recent years the seed supply in this region has decreased considerably, especially around Cat Ba Island.

Central region (from Quang Binh to Khanh Hoa)

Yellowtail fry are caught between November and March with a peak in January and February.  The maximum amount of fry caught in this area is between 80,000 and 100,000 pieces annually.  Landings of fry in 1991/1992 and 1992/1993 were 83,000 and 37,000 pieces respectively.  Red-spotted grouper (E. akaara) and greasy grouper (E. tauvina) are the most common species in the Nha Trang area and more than 100,000 fry are caught each year.  Also seabass (Lates calcarifer) fry are freely available as it is considered a pest in the lagoons used for extensive shrimp farming.  In the Cam Ranh Bay (south of Nha Trang), fishers can catch 10 to 15 kg per day of grouper fry with an average size of 70 g/piece.  The main catching season is from March to August, although fry are caught year-round.

Southern region

No data are available regarding the potential catch from Ninh Thuan to Kien Giang province in the southern part of Vietnam.

Throughout Vietnam, fry catching methods are very simple.  Normally, fishers use hooks, longlines, traps, push-nets and trawls to collect grouper and snapper fry.  In case of seabream and yellowtail they are normally caught using a beach seine or lift net.  The supply of marine seed will limit the growth of marine fish cage culture in Vietnam.   The technology is not yet available for the artificial propagation of grouper, mudcrab, and lobster on a commercial scale, although research continues at Cat Ba island and in other countries.  In the meantime, the farming of these species is dependent on wild stocks.  Fisheries for the seed of high value marine fish are not adequately monitored or controlled.  In the absence of controls, stocks may be over-fished, with severe implications for the environment and sustainable development of the industry.  Under these circumstances it is difficult to recommend expansion of these enterprises prior to proper assessment of impacts and sustainable yield.

Since 1993, the Research Institute of Marine Products (RIMP) of the Ministry of Fisheries has carried out some experiments on artificial seed production of marine fish.  Grouper, snapper and black kingfish (Rachycentron canadum) were bred in 1994 and 1995.  The hatching rate ranged from 40 to 85%, but survival rate of fry was too low (under 1%).  The results of the larval rearing during 1995 are shown in Table 2.

Table 2.  Grouper larvae rearing results from RIMP research during 1995

Date

Number of larvae

Avg temp (ToC)

Avg salinity (o/oo)

Survival time (days)

04/28

05/01

05/02

05/03

05/07

05/09

05/10

05/11

05/21

05/22

05/29

05/31

06/04

06/07

06/12

06/20

06/21

234,000

17,000

19,000

64,000

20,000

13,000

86,000

349,000

147,000

57,000

245,000

201,000

26,000

12,000

6,000

50

89,000

28.0

29.0

30,0

30.0

27,0

27.2

27.8

28.0

28.5

29.5

31.0

31.5

30.5

30.0

27.5

30.0

32.0

30

30

30

30

31

32

31

31

32

32

32

31

31

31

30

30

30

60

4

14

3

2

7

9

8

12

6

6

7

60

3

2

1

5

 

1,584,000

 

 

 

 

Larvae were fed 4 times a day on oyster eggs, rotifer and Artemia depending on the stage of larvae.  The studies on artificial seed production of grouper, snapper and black kingfish have been initially successful, however, many technical problems in the early stage of larvae rearing must be solved.  A marine fish hatchery, which should commence operation in 1997, is under construction in Cat Ba Island.

Trash fish and prepared feed are the main food sources used for grow-out.  In the southern and central part of Vietnam, there are 24 feed production units with total capacity of 47,000 tonnes per year for shrimp and brackish water fish culture.  SEAPRODEX Da Nang has a pelleted feed producing plant with a capacity of 2,000 tonnes per year.  The majority of the production is shrimp feed including two types: one for semi-intensive farming in the central region and a small amount of high quality feed for two intensive shrimp farms in the Mekong river delta.  Until now, most feed used for marine fish culture is “trash” fish.  Only a small amount of prepared feed, imported from Japan, is used for yellowtail fry raising in the Da Nang area.  At present in Vietnam, capture fisheries provide about 800,000 tonnes of fish per year, of which 200,000 tonnes or a little more are classified as low value trash fish.

Trash fish includes the following fish species: spotted sardine (Sardinella jussieu), round scad (Decapterus maruadsi), tiger fish (Therapon theraps), lizard fish (Saurida spp.), commersonis (Stolephorus commersonii), pony fishes (Leiognathus spp.) and the juveniles of a range of species, including table fish species.  Trash fish is a common marine fish feed in Vietnam, particularly for cage-cultured fish and for shrimp.  The heavy use of trash fish in ponds and cage culture can contribute to poor feed conversion and can be highly self-polluting.

Food conversion ratios (FCRs) for grouper in Vietnam range from 6 to 20:1 depending on the type of feed and feeding regime.  FCRs for yellowtail fry are rather low, remaining between 2 and 3:1 because of the use of commercial feed from Japan.  In general, cage farmers appear to have little experience in proper feed management, resulting in poor food conversion.

Sustainable development of coastal aquaculture in Vietnam requires that close attention be given to the identification and control of shrimp and fish diseases.  The high losses from shrimp disease can be reduced by introduction of more effective health management practices.  The potential economic and environmental benefits provide strong justification for such measures.  At present there are too few well-trained scientists and technicians available for the research and development in shrimp and fish disease control.  Modern diagnostic facilities are also generally lacking, particularly basic field equipment which can be used at farm level to investigate disease outbreaks, collect samples in a proper way and diagnose farm-level problems.  The strengthening of human resources and facilities requires urgent attention to deal with present and anticipated future problems related to shrimp and fish disease.  Environmental problems faced by farmers include losses due to damage in exposed sites, and some water pollution problems, leading in Ha Long Bay to some fish mortalities from localised water quality deterioration.  Such problems can be avoided by selecting locations with sufficient water change, and ensuring stocking levels and cage numbers are within the capacity of the local environment.

There are risks under present management systems of introducing new diseases to aquaculture environments.  The ordinance on the "Conservation and Management of Marine Resources" states that Ministry of Fisheries has the responsibility for decisions concerning the introduction and breeding of new species in Vietnam.  However, limited capacity exists to analyse and support such decisions at the present time.

For stocking of cages, fish fingerlings smaller than 10 cm are stocked at 70-80 pieces/m3 and fish of 10-18 cm are stocked at about 50-60 pieces/m3.  The bigger fish (>20cm) are kept with a density of 30 pieces/m3.

From 1992 to 1995, RIMP has carried out some studies on the technology of grow-out culture and artificial breeding.  The study results showed that the growth rate of grouper, snapper and yellowtail reared in floating net cages is rather good.  The growth rate per month for grouper is 60 to 80g, and for snapper and for yellowtail is 90 to 100g and 250 to 280g, respectively.  Kingfish in particular has a high growth rate of 300 to 400g/month.  Seabass has been grown in ponds and their growth rate is about 100 to 130g/month (seabass are fed live Tilapia kept in the same ponds).

Environmental aspects and management

The exploitation of coral reef fishes in Vietnam is not thought to be a big problem, because the coral reef fisheries are relatively unexploited.  Only some ornamental fish companies carry out activities, collecting high value fish by divers using SCUBA with traps, hooks or hand held scoopnet at depths of 6 to 40 metres in the Nha Trang area and around the Spratly archipelago.  Some foreign joint ventures use toxic sodium cyanide to catch fishes such as grouper, snapper, wrasses and other fisheries, and some fishermen use illegal explosives for fishing.

Cyanide affects far more than just the target species.  Smaller fish and shellfish are less resistant to cyanide, and many die for each target fish captured.  Moreover, corals, which provide the basic foundation of the reef community bleach and die.

There is little primary data available on the environmental impacts of aquaculture in Vietnam.  Research on the environmental impacts and management of coastal aquaculture should be encouraged, in order to properly define impacts and management protocols for different aquaculture systems and coastal environments.  Coastal aquaculture should make environmentally sustainable use of land and water resources, and be properly integrated into exiting agricultural and ecological systems, such as agricultural farms, watersheds and coastal areas.  To maximise the social and economic benefits of aquaculture development in local communities and to avoid social conflict and conserve natural resources, the process of aquaculture development must carefully consider the needs of all resources users.  Thus, local and national government should encourage and facilitate participation of the public, communities and industry in formulating policies and guidelines for aquaculture development, within the carrying capacity of the coastal environment and in harmony with other local users of common resources.

Effluent and water quality standards for aquaculture and coastal areas should be viewed as medium to longer-term objectives.  The Ministry of Fisheries should coordinate efforts with the Ministry of Science, Technology and Environment, and other concerned agencies for a comprehensive coastal water quality management scheme, to ensure a comprehensive coverage of coastal water quality.  The application of environment impact assessment (EIA) can be used to guide environmentally sustainable investment decisions.  The regular environmental monitoring of coastal areas can also help provide early warning of any harmful environmental changes in aquaculture areas.

Marketing and economic aspects

Grouper prices are currently high, with an average domestic price of around US$10 per kg.  Even this level is low by international standards, and some increase may be obtainable through negotiation with Hong Kong buyers.  Farm size is variable, ranging from small farms with 2-4 cages up to major enterprises with 60 or 100 cages.  On an area basis, grouper culture is estimated to produce gross revenue of the order of US$160 per m2 with total production and overhead costs amounting to about US$130 per m2.  Margin is a relatively low 19 percent of output, suggesting that the activity be at potential risk due to price or cost factors or mortality.  The main constraint facing the activity at present is difficulty in obtaining fry in some areas and some seasons.  It is quite likely that commercial hatchery technology will overcome its technical difficulties in the next five years or so, which would assist in alleviating the seed constraint.  It is likely that the development of hatchery technology will reduce the economic viability of grouper farming.  When the current reliance on wild fry for stocking and trash fish for feed is taken into account, it is not considered that substantial effort is merited by the government to promote the development of grouper farming, without concurrent investments in hatcheries and feeds.

The marketing channels for aquaculture products are varied.  Since the introduction of market reform, entry to the marketing industry has been more or less unrestricted.  This has resulted in a rapid increase in the number of middlemen servicing the sector.  While marketing systems and the degree of competition will develop overtime, it is considered that the small business skills of the Vietnamese represent strength to be capitalised on.  Where any niche is identified in the marketing and distribution chain, it is likely that it will be filled rapidly, particularly if the entry capital needs are limited.  At the same time, the government needs to monitor marketing and to assist in removing market imperfections.

Constraints to grouper and coral reef fish aquaculture

There are several major constraints for the development of marine fish farming in Vietnam, most of which can be traced to the lack of capital and knowledge related to marine fish farming.  There is a need for technology related to the production of fry, as well as cage farming in the sea.  So far the low availability of marine fish fry has limited the development of marine fish farming.  Both the variability and insufficient number of wild caught fry will not sustain a long-term development of sea cage farming.  Without hatcheries and nurseries, the scope for marine fish farming is limited.  Also sea ranching to increase the natural fish stocks by release of artificial produced fry depends upon stable supplies of fry in high numbers.

Long term education and training seem to be the most important factors for a sustainable development of marine fish farming in Vietnam.  Development further implies the use of technology adapted to Vietnamese conditions, and an optimal use of available resources for fish feed.

After the problem of fry, the availability and quality of feed is regarded as the most serious constraint to the farming of marine fish.  At almost all fish farms, the fish are fed daily when trash fish was available.  The use of trash fish creates environmental problems, which has probably led to some of the diseases encountered.  To develop marine fish farming on an industrial scale, together with usage of trash fish, it is necessary to have many fish meal units to produce enough pelleted feed for aquaculture.  The other constraints for marine fish farming include:

·         lack of planning of culture areas, which can result in potential ecological and environmental problems

·         the unsatisfactory development in the culture of export species, resulting in low yields

·         limited scientific research findings, especially in relation to artificial seed and prepared feeds, to increase production

·         high economic risk due to new technology; no insurance is available for farmers who may lose their equity or working capital and be forced out of business or to borrow from moneylenders at high interest rates

·         severe storms and typhoons are a major constraint to coastal aquaculture in the north and central part of Vietnam

·         lack of fish disease diagnosis and treatment

Recommendations to deal with constraints

The main recommendations include:

·         Research is essential to identify and help remove constraints to aquaculture development in Vietnam.  Research budgets are currently inadequate to allow the institutions to operate effectively.

·         Long term education and training for young scientific and technical staff are very important in order to develop marine fish culture in Vietnam.

·         The production of marine fish seed must be established both in quality and quantity if the fish farming industry is to develop in a sustainable manner.

·         The development of the coastal aquaculture sub-sector requires the clear, well-formulated, and implementable national and local policies and is based on a full consideration of financial, socio-economic, and environmental sustainability.

·         Research institutes and University should be encouraged to establish links with other regional institutes involved in coastal aquaculture research, as there is much relevant research work going on which would be useful to Vietnamese scientists.  Such cooperation, possible through the Network of Aquaculture Centres in Asia- Pacific (NACA) and other regional organisations, would be cost-effective for Vietnam, and would help avoid repeating research.

·         The introduction of technologies to Vietnam should be undertaken with care, ensuring compatibility with local environments and farming systems.

 

References

Ministry of Fisheries, 1992.  Direction and objectives for Vietnam fisheries development during 1991-2000 period.  Report presented at the Vietnam Fisheries Development Workshop, Ha Noi, May 5-7,1992.  8 pp

Svennevig, N. and H. Reinertsen, 1994.  Prefeasibility study of marine finfish farming in Vietnam.  SINTEF Report STF21 F94021, 43 pp.

Son, D. M., 1995.  Floating net cage marine finfish culture.  Report presented at the training course on fisheries extension activities, Hai Phong, August 1995.  8pp.

Son, D. M., 1995.  The technical studies on seed collecting and production, grow-out culture and live transport of grouper, snapper and yellowtail.  Final report of national project "KN.04.06".  119 pp.

Son, D. M. and T.V.  Quynh, 1995.  The present status and future prospects of fish and shrimp culture in Vietnam.  In C. S.  Lee (ed.) Status, constraints, and future prospects of aquaculture in Asia.  Tungkang Marine Laboratory Conference Proceeding 5.  1996.

SCP Fisheries Consultants Australia, 1996.  Coastal Aquaculture Development Project.  Volume II.  Coastal Aquaculture Sector Review.  Asian Development Bank and Ministry of Fisheries, Hanoi.

Thuoc, P., 1995.  Fish resources ofcoastal zone in Vietnam and recommendations for preserving of resources stock in the coastal zone.  Unpublished Vietnam Country Report

 



[1] Research Institute of Marine Products, Hai Phong, Vietnam