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Viet Nam is a nation in Southeast Asia. It borders the People's Republic of China to the north, Laos to the northwest and Cambodia to the southwest. To the country's east lies the South China Sea. With a population of approximately 84 million, Viet Nam is one of the most densely populated nations in Southeast Asia.

The earliest record of seagrass in Viet Nam was in 1885 when Balansa discovered Halophila ovalis and H. beccarii in the Song Hong Meo River (now part of the Ruot Lon River) near Quang Yen District, Quang Ninh Province (Van Tien 2008).

There are 14 species of seagrass reported in Viet Nam (Cymodocea rotundata, Cymodocea serrulata, Enhalus acoroides, Halodule pinifolia, Halodule uninervis, Halophila beccarii, Halophila decipiens, Halophila minor, Halophila ovalis, Ruppia maritima, Syringodium isoetifolium, Thalassia hemprichii, Thalassodendron ciliatum and Zostera japonica).

Viet Nam is at the overlap of temperate and tropical seagrass species with Zostera japonica growing intertidally in the north and mixing with Halophila ovalis, while in the south the species composition is similar to the Philippines and Malaysia. Ruppia maritima is common in coastal zones in northern Viet Nam, Halophila ovalis is widespread in coastal zones and around islands in north and central Viet Nam, and Halodule pinifolia is particularly prevalent in southern areas of Viet Nam.

The total area of seagrass in Viet Nam is estimated at 17,675ha (Van Tien, Pers. Comm. 23Mar10). Seagrass medaows are distrubuted along the entile coastline with meadows occurring from Viet Nam’s northern border with China, through to the south-western border with Cambodia, but mostly from the middle of the southern sections. Their status is unknown though in general the Vietnam coastal zone has been heavily impacted by sedimentation and domestic and agricultural pollution. 

Seagrass meadows in Viet Nam have suffered serious degradation, with approximately 45 to 50% of their areas lost over the past 2 decades. Threats to seagrasses in Viet Nam include both natural and human induced. Natural threats in include typhoons (Tonkin Gulf in northern Viet Nam experiences an annual average 35 typhoons), turbidity and sedimentation (river runoff from agriculture, foresty, and urban development) and freshwater runoff (particularly during the rainy season). Human-induced threats include destructive fishing methods (eg explosives, trawling, gill net, drift net, bottom net, blanket nets, fine square nets, electro-fishing, cyanide trampling, gleaning, and digging), aquaculture (construction of ponds on tidal flats), coastal construction (eg roads, bridges, houses, ports and dredging), pollution (eg wastewater discharges composed of heavy metals, suspended sediments, nutrients, and oils), and reclamation of tidal flats for agricultural purposes. The main causes of seagrass degradation stem from low awareness and unstable economic conditions.

Seagrasses in Viet Nam are important either for direct use or as habitat. The majority of exploited seagrasses (particularly Zostera and Ruppia) are used as feed for livestock and fertiliser. The main importance of seagrass is however as the use of associated biota, such as algae (eg Gracilaria spp of commercial value), harvesting of the swimming crabs (Portunus pelagicus and P. sanguinolentus), sea cucumbers (commercially important species Holothuria scabra and Halodeima atra), fin fish (at least 34 commercially important species), and seahorses (in particular Hippocampus kuda). Seagrass in Viet Nam is also important as food for dugongs (Dugong dugon) and green turtles (Chelonia mydas).

Until recently, it was widely considered that the only remaining population of dugongs in Viet Nam inhabited areas of Con Dao National Park, an archipelago of 14 islands in the southern province of Ba Ria-Vung Tau. The major threats to dugongs in Viet Nam are hunting (not widespread), gill nets and starvation through habitat destruction.

Seagrass monitoring in Viet Nam is also conducted are part of the UNEP/GEF project reversing environmental degradtion trends in the South China Sea and Gulf of Thailand (www.unepscs.org).

For more detailed information on seagrasses in Viet Nam, see Van Tien (2008)

 

Con Chim

 

Monitoring: ongoing, biannual

Principal watchers: Binh Dinh Fisheries Department

Past: Gail Begbie
Location: Con Chim Marine Sanctuary, northern section of
Site code: CT1, CT2, CT3

CT1 position: N13.84868 E109.23258 (heading 165 degrees)

CT2 position: N13.85251 E109.24000 (heading 190 degrees)

CT3 position: N13.85057 E109.24020 (heading 145 degrees)

Best tides: 0m
Issues: land runoff, coastal development, land reclamation, sewage, shellfish digging,
Comments: The Con Chim Marine Sanctuary (CCMS) run by the Binh Dinh Fisheries Department covers 480 ha in the 5060ha estuary of Thi Nai. It is designed around the participation of three coastal communes that rely almost entirely on the marine resources of Thi Nai Lagoon for their livelihoods.

Status (Dec08):

  • Two sampling events were conducted in 2007.

 

 

 

 

Con Dao

 

Monitoring: proposed

Principal watchers: Bronwyn Cumbo & Wildlife At Risk
Location: Con Dao National Park
Site code: CD
Issues: sedimentation from coastal development
Comments: include 16 big islands about 230 kilometres from Ho Chi Minh City. A biodiversity hotspot. Due to the combined influence of “Typhoon Linda” and human-induced impacts, 20 to 30% of Con Dao’s seagrass areas are reported to have been lost.

Seagrasses in Con Son Bay (Con Dao Island, Ba Ria-Vung Tau Province) are reported to be distributed from the low tide level to a depth of 10 to 15m: H. pinifolia, H. uninervis, H. ovalis, T. hemprichii, C. serrulata, S. isoetifolium, H. decipiens, and H. ovalis, respectively. H. decipiens and C. serrulata are often found at depths of 15 to 20m.

Con Dao National Park is the only known location in Viet Nam where regular dugong sightings occur. The estimated number of dugongs in the Con Dao area is around 10 individuals. From 1997 to 2002, 10 dugong mortalities occurred in Con Dao. Scientists now believe that this population is at a high risk of local extinction within 5 to 10 years.

Con Dao is also the most significant nesting area for Green turtles (Chelonia mydas) in the country. Marine turtle nesting beach programmes have been carried out in Con Dao National Park since 1995 with approximately 250 individuals nesting each year. Green turtles of Con Dao feed on Thalassia hemprichii and Halophila ovalis.

 

 

 

 

 
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