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4. MARINE RESOURCES MANAGEMENT FOR SEA FARMING AND RANCHING


4.1 Survey of Marine Bio-Resources
4.2 Legislation for Management and Protection of Aquatic Resources
4.3 Research on Genetics and Biodiversity
4.4 Disease Prevention and Health Management
4.5 Marine Habitat Improvement
4.6 Reorganization of the Fishery Sector

The seas of China cover a huge area from the Bohai Sea, Yellow Sea, East China Sea until the South China Sea. There is no main warm or cold current passing through these areas and there is no strong upwelling. Therefore, the distribution and configuration of existing marine organisms are rather specialized and limited. In comparison with the majority of the world fishing grounds, Chinese marine resources are characterized by a relatively greater number of species and smaller biomass.

Since the 1980s and particularly in the 1990s, research on marine resources was intensified. On the basis of results, measures for the management of marine resources were taken into three directions: (i) implementation of a survey of existing marine bio-resources; (ii) formulation of the legislation necessary for managing and protecting natural aquatic resources; and (iii) intensification of research on genetics and biodiversity of these resources

In addition, measures were taken in three other fields: (i) disease prevention and health management for farmed species; (ii) marine habitat improvement; and (iii) reorganization of the fishery sector..

4.1 Survey of Marine Bio-Resources

Since 1950, the Chinese government became increasingly interested in supporting research on marine fishery resources and several reports were published until the 1960s. This provided important data for genetic resources management and biodiversity protection. In 1979, the State Council approved the “Report of the National Workshop on Agricultural Resources Investigations and Agricultural Zoning”. Accordingly, in 1980, the National Bureau of Aquatic Products nominated a group of experts to carry out a detailed survey of existing fishery resources and their regional organization.

Survey results for the Guangdong Province may be summarized as follows:

This survey of the marine fishery resources provided valuable data for policy making, design of research projects and future investments. It was also proved that it contributed significantly to the stable development of sea farming and sea ranching in China.

4.2 Legislation for Management and Protection of Aquatic Resources

Table 32. Main legislation issued by the Chinese government

Bylaws and regulations

Issued by

Year of issue

Temporary Bylaw on Reproduction and Protection of Fishery Resources (Draft)

Ministry of Fisheries

1957

Trial Measures on Reproduction and Protection of Penaeus chinensis in the Bohai Zone

Drawn up by Ministry of Fisheries; Approved/issued by State Council

1962

Direction on Active Protection and Rational Utilization of Wild Animal Resources

State Council

1962

Survey on Marine Fishery Resources

Organized by Ministry of Agriculture & Forestry

1971

Summary on Prevention and Treatment of Pollution in Bohai Sea and Yellow Sea

Report approved by State Council

1977

Bylaw on Reproduction and Protection of Fishery Resources

State Council

1979

Notification on “Standards of Water quality for the Fishery Industry”

State Council Leading Team for Environmental Protection, State Committee of Construction, State Committee of Planning, General Bureau of Fisheries

1979

Regulations on the Reproduction and Protection of Fishery Resources in the Bohai Area

General Bureau of Fisheries

1981

Law on Environmental Protection of Sea and Ocean in China

Adopted by 5th Standing Committee of National People’s Congress

1982

Levy and its Use for the Propagation and Protection of Fishery Resources

Drawn up by Ministry of Agriculture, Ministry of Finance, and National Bureau of Materials. Approved by State Council.

1988

Law on Protection of Wild Animals

President Yang Shangkun

1988

Administrative Measures for Natural Protection Zones of Aquatic Plants and Animals

Ministry of Agriculture

1997


As early as the 1950s, the Chinese government turned its attention to the protection of natural resources. In 1951, the State Council approved the “Temporary Fishery Bylaw for the Mid South Region” and the “Temporary Regulations on the Reproduction and Protection of Aquatic Plants and Animals in the Mid South Region”. Later, a series of important regulations and bylaws were also approved and issued, as shown in Table 32.

The regulations and bylaws listed above clearly show that the protection of natural resources, including fishery resources, and the conservation of their biodiversity have been part of China’s basic policy for development.

On the basis of this legislation, fishery authorities drew up and issued a series of measures for the protection of spawning grounds and of areas used by larvae and juveniles. This played an important role for ensuring the sustainable development of the fishery industry.

4.3 Research on Genetics and Biodiversity

To ensure the protection of natural resources, it was also necessary to have a basic knowledge of existing indigenous species, of exotic species and of their valuable varieties. At present, Laminaria, Porphyra, flounder, Japanese perch and hard-shell clam have been well studied, which should help protecting these natural resources and providing excellent varieties for mariculture. Research was also carried out on genetic improvement such as polyploid breeding and on karyotype determination for economically important mollusc and fish species (Tables 33 and 34).

In the 1960s, several new varieties of Laminaria japonica were bred, with new characteristics such as higher level of iodine and better growth rate. This enabled China to eliminate a serious iodine shortage and to develop the seaweed processing industry. Since the 1990s, polyploid varieties of abalone, oyster and scallop were produced. Such research benefited mariculture and increased seafood production.

Table 33. Karyotypes of selected marine molluscs

(st type calculated in double-arm)

ORDER

Family

Species

2n

Karyotype formula

NF

ARCHAEOGASTROPODA

Haliotidae

Haliotis discus hannai

36

22m+14sm

72

NEOGASTROPODA



Buccinidae



Neptunea arthritica cumingii

60

30m+22sm+8st

112

Buccinum pemphigum

30

16m+10sm+4st

56

Plicifusus scissuratus

34

20m+10sm+4st

64

ARCOIDA



Arcidae



Scapharca sp.

38

12m+20sm+6st

76*

S. subcrenata

38

14m+22sm+2st

76*

Tegillarca granosa

38

28m+10sm

76

MYTILOIDA





Mytilidae


Mytilus edulis

28

12m+10sm+6st

50

M. coruscus

28

12m+10sm+6st

50

Pectinidae

Chlamys farreri

38

6m+10sm+22st

54

Ostreidae


Crassostrea talienwhanensis

20

20m

40

Crassostrea sp.

20

12m+8sm

40

PTERIOIDA






Pteriidae






Pinctada martensii

28

14m+6sm+6st+2t

48

P. maxima

28

16m+4sm+6st+2t

48

P. margaritifera

28

14m+6sm+8st

48

P. nigra

28

4m+4st+20t

32

P. radiata

28

4m+4st+20t

32

P. chemnitzi

22

8m+2sm+2st+10t

32

VENEROIDA




Solenidae


Solen strictus

38

30m+6sm+2t

74

Sinonovacula constricta

38

26m+6sm+2st+4t

76

Veneridae


Meretrix meretrix

38

18m+20sm

76

Ruditapes philippinarum

38

28m+10sm

76


Table 34. Karyotypes of selected marine fish

ORDER

Family

Species

2n

Karyotype formula

NF

ANGUILLIFORMES


Congridae


Conger myriaster


38

8m+10st+20t

56


10m+10sm+18t

58

MUGILIFORMES








Mugilidae



Mugil cephalus

48

48t

48

Liza haematocheila

48

48t

48

Lateolabrax japonicus

48

48t

48

Serranidae



Epinephelus sexfasciatus

48

2sm+46t

50

E. awoara

48

48t

48

E. fario

48

14m,sm+34st,t

62

Sciaenidae


Nibea albiflora

48

48t

48

Sciaenops ocellatus

48

48t

48

PERCIFORMES



















Pagrosomus major

48

2st+46t

48

Sparidae


Sparus macrocephalus

48

4m+4sm+2st+38t 6m+4sm+38t

56 58

S. latus

48

4m+2sm+4st+38t

54

Pomadasyidae


Hapalogenys mucronatus

48

2m+8sm+14st+24t

58

H. nitens

48

2m+8sm+2st+36t

58

Stichaeidae


Ernogrammus hexagrammus

48

48t

48

Thunnus alalunga

48

2m+4sm+42t

54

Thunnidae


T. albacora

48

2m+2sm+2st+42t

52

Katsuwonus pelamis

48

48t

48

Gobiidae




Tridentiger trigonocephalus

44

10m+28sm+2st+4t

82

Chaenogobius annularis

44

20m+22sm+2t

86

Glossgobius fasciatopunctatus

46

16sm+6st+24t

62

Synechogobius hasta

44

2m+42st,t

46

Periophthalmidae


Boleophthalmus pectinirostris

46

2st+44t

46

Sebastes schlegeli

48

2m+46t

50

Scorpaenidae



S. hubbsi

48

3m+2st+43t (fem)

51

S. nigricans

48

2m+46t

50

Sebatiscus marmoratus

48

2m+46t

50

SCORPAENIFORMES







Hexagrammidae



Agrammus agrammus

48

8m+32sm+8st (fem)

88



7m+33sm+8st (male)

88

Hexagrammos otakii

48

6m+16sm+20st+6t

70

Platycephalidae

Platycephalus indicus

48

2m+8sm+2st+36t

58

Paralichthyidae



Paralichthys olivaceus

48

48t

48

Pseudorhombus cinnamomeus

48

48t

48

Pleuronichthys cornutus

48

12m+2sm+34t

62

PLEURONECTIFORMES




Pseudopleuronectes yokohamae

48

48t

48

Pleuronectidae


Kareius bicoloratus

48

48t

48

Microstomus achne

48

48t

48

TETRAODONTIFORMES


Aluteridae

Navodon septentrinalis

40

40t

40

Tetraodontidae

Fugu rubripes

44

20m,sm+24st,t

64

4.4 Disease Prevention and Health Management

Since the 1980s, the spread of viral diseases of penaeid shrimp resulted in major losses of production world-wide. As this affected fishery sustainable development, interested authorities, researchers and investors concentrated their efforts on finding a solution to the problem.

In China, production of farmed penaeid shrimp suddenly declined from over 200 000 mt in 1992 to 80 000 mt in 1993. Even though important funds were invested in research, shrimp production never reached its highest historical record again. Almost all other farmed species such as marine fish, scallop, oyster and seaweed were also affected by diseases, at various intensity levels. Financial losses exceeded one milliard RMB annually. These diseases were diagnosed as being caused by a wide variety of pathogens, ranging from bacteria to viruses, from fungi to parasites.

These disasters occurred for three main reasons:

Before 1992, there was no effective measures to protect farm stocks from diseases. But since the huge losses of farmed penaeid shrimp in 1993, various prophylactic and therapeutic measures were taken to protect farmed species in the long term.

These measures, which exerted a profound influence on the sustainability of sea farming and sea ranching development in China, were as follows:

All these actions contributed effectively to control shrimp epidemics and diseases of other marine species. In general, epidemics prevention in aquaculture and healthy management in sea farming were considered to be essential for the sustainable development of sea farming and ranching.

4.5 Marine Habitat Improvement

In the 1980s, artificial reefs were built in China. Due to financial constraints, the project was stopped after five years (Section 3.7). Existing habitat improvements gave good results for the ranching of sea cucumber (Stichopus japonicus), Japanese scallop (Patinopecten yesoensis) and abalone (Haliotis discus hannai), as well as for the protection of mangroves.

The main measures included (i) establishing protected zones; (ii) Improving natural habitats of economically important species; (iii) stocking seed in these natural habitats for resource enhancement; and (iv) prohibiting cutting and damaging mangroves.

In 1999, the National Council approved five natural sea protection zones. Among them, the Natural Sea Protection Zone of Nanji Islands was placed on the United Nations list of the Network of Protection Zones of the Biosphere. In this zone, there were about 1 500 marine aquatic species (mainly, 421 molluscs and 178 macroalgae) to be properly protected. In addition to these national zones, provincial and municipal governments approved many small-scale protection zones for enhancing and protecting local indigenous species in particular.

Habitat improvement was done on a trial basis, combining environmental improvement with stocking of seed. In the Shandong Province, such an enhancement zone for sea cucumber was established, involving the introduction of stones or concrete structures at selected sites and the stocking of juveniles in these areas.

A penaeid shrimp (P. chinensis) enhancement project was carried out in the 1980s. A return rate as high as 8 to10 percent was reported for the Buhai Sea and the Xiangshan Bay (East China Sea). The project was stopped to prevent any risk of disease epidemics and for other reasons.

Protection of the mangrove forest became a priority world-wide, similarly to the protection of coral reefs. The Chinese government focused its attention on this subject also, following reports that of the 60 000 ha of natural mangroves which once flourished along the coastal line from the Fujian Province to the Hainan Province, only 10 000 ha subsisted. New regulations forbade mangrove cutting and reforestation was planned.

4.6 Reorganization of the Fishery Sector

According to statistics, the labour force engaged in marine fishing steadily decreased from 1.19 million in 1997 to 1.18 million in 1998, an average annual rate of about 0.8 percent. On the contrary, the labour force engaged in sea farming regularly increased from 459 000 in 1997 to 488 000 in 1998, an average annual rate of 6.3 percent. It meant that a great part of the labour force engaged in marine fishing shifted to mariculture activities. During such period, fisheries authorities paid more attention to the reorganization of the fishery sector and to the redeployment of fishermen.

To support such reorganization, there were three possibilities: (i) developing offshore cage farming; (ii) establishing land based marine farms; and (iii) developing the fishery processing industry.

For example, research on offshore cages was listed as one of the national priority projects since the 1990s. In the Zhejiang Province, a special team was organized to study the introduction of offshore cages from other countries, such as the USA and Norway, and the manufacture of locally designed equipment. Similar activities took place in the Guangdong, Fujian, and Shandong Provinces.

In northern China, the difference between minimum and maximum sea water temperatures can be as high as 20 to 25 C and it is difficult to farm marine fish in the open sea. Fishermen, therefore, easily accepted to farm marine fish in land based facilities. Flounder and European turbot became popular fish for sea farming. In order to prevent water pollution from commercial-scale farms, advanced recirculation systems were adopted.

It is our believe that the shift from fishing to farming will be successful because sea farming and sea ranching are firmly established activities in Chinese fishing towns and villages. Regulations and policies also encourage entrepreneurs to invest in this prosperous industry.


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