New Data on Spatio-temporal Stability and Variability of the Vietnamese Reefs
Received Date: Mar 14, 2015 / Accepted Date: Apr 23, 2015 / Published Date: Apr 26, 2015
Research work on reefs of open South-China Sea and clause bay (South Vietnam), and the Gulf of Thailand investigated in the beginning of the 80s of the previous century were conducted in 2005-2007. A distinct dependence of the level of coral communities’ degradation on their closeness to settlements and aquaculture areas were established. Appreciable changes due to anthropogenic impact have occurred on the reefs that are the nearest to the city. There was a reduction in substrate cover by reef-building corals, a substitution of dominant scleractinian species, and a decrease in the numbers and diversity of common species of corallobionts. The index of species diversity for scleractinian also decreased. The seaweeds Chnoospora and Halimeda spread into all zones of the reefs. Changes in coral communities on more distant and protected reefs were not so marked
Keywords: Reef; Community; Stability; Variability; Vietnam
The first studies of reefs of Vietnam, R. Serene held at the end of the 1930s , then Dawydoff  went on the reef study. The works of these scientists were related to describing the species richness of corals and other invertebrates in reefs of the South Vietnam. Since the 1980s, as a result of joint Soviet-Vietnamese marine and land expeditions, as well as thanks to the World Wildlife Fund, the systematic comprehensive studies of different types of reef species composition and structure of reef communities in the region began [3-9]. The last decade of this century, repeated studies were conducted on the same transects of previously studied reefs [10-13] which, on the one hand, revealed significant changes over a quarter century in the species composition and structure of some reef communities, on the other hand, corroborated a satisfactory sustainability of some reefs. Beyond, during the expeditions of recent years, 16 species of reef-building scleractinian previously unknown in reefs of Vietnam have been found.
In 2005 and 2007, the expedition of the A. V. Zhirmunsky Institute of Marine Biology FEB RAS on research vessel “Akademik Oparin " again explored a number of visited coral reefs, species composition and structure of the population which were first described by a quarter of a century ago (Figure 1). Examined reefs differ by geomorphology, degree of wave effect and connection with open sea, in accordance with which they classified as reefs of open capes and islands, reefs of closed bays, and reefs of channels [14-16].
Figure 1: Schematized map of the surveyed regions. 1: Bai Tu Long Archipelago; 2: Ze Island; 3: Cape Danang, Cham and Son Tra islands; 4: Re Island; 5: reefs of the Khanh Hoa Province; 6: Thu Island; 7: Ca Thuik Islands; 8: Con Dao Islands; 9: Tho Chu Island; 10: An Thoi Archipelago and Namsu Islands; 11: Rach Gia bay; 12: Royal Bishop and Astrolab shoals; 13: Spratly Islands.
In the first decade of the twenty-first century, there have been repeated studies on the same sections of the previously studied reefs [11-13] to determine their status. These studies showed, on the one hand, the significant changes in a quarter of a century in the composition and structure of some species of reef communities and on the other hand confirm satisfactory stability of some reefs. Also during the expeditions of recent years were found 16 species of reef building scleractinian that were previously unknown in the reefs of Vietnam. Because of the identified species, richness of corals of the Vietnam has increased by more than 4% and totaled 376 species.
Materials and Methods
From 1982 to 2005, these reefs did not change very much in their species composition and community structure. Diversity of Acropora, totaling not less than 30-35 species, remained high as before. The bulk of species diversity, as on the most Indo-Pacific reefs [16,19,20], formed by scleractinian from five families: Acroporidae, Faviidae, Fungiidae, Poritidae and Dendrophylliidae, making more than 60% of their total number. Representatives of five genera – Acropora (15-20 species), Montipora (10-15), Porites (11-13), Favia (7-10) and Fungia (7-10) – are the most diverse and numerous in coral communities of these reefs. For the recent twenty years, the area of substratum covering by corals was substantially reduced on these reefs (down to 10-30%). Small massive coral colonies (5-10 cm), mainly from Faviidae and Poritidae families, began to prevail noticeably in the community structure of the reef slope (not more than 3-5 colonies per sq. m). Silting of substratum, which even can be clearly visualized, increased due to closeness of a big number of mariculture installations. In addition to that in all areas of intensive mariculture development active aggression of predatory gastropoda Drupella rugosa, which density is from 8-20 individuals per a colony of 10 × 13 × 18 cm size to 3000 individuals in some aggregations of branched Acropora colonies, against various scleractinian species of Acropora, Porites and Montipora genera was observed.
A reef near Mju Island attributed to the channel between the densely populated islands. It situated in the immediate vicinity to Nha Trang city and port, which surrounded from every quarter with mariculture farms and tourist complexes. Here the changes in reef community composition are especially obvious due to heavy silting of substratum, corals and other representatives of macrobenthos in the area of the reef slope. In the surrounding waters, values of sedimentation flow are extremely high: 35.3-48.6 g·m2·day-1. For the past two decades the degree of substratum covering by corals reduced, number and size of colonies of reef-building scleractinian decreased, and abundance of algae Halimeda opuntia, H. discoidea and Ch. implexa increased. Species diversity of corals, especially of Acropora, reduced. Various species of lamellar and branched Acropora and Montipora, common here earlier, were considerably replaced by monosettlement of fine-branched Montipora porites. Alga Ch. implexa settled in all reef zones, occupying actively substratum and space between coral branches, and its covering made 60-75% of substratum area (Figures 2-4). Coral covering of substratum overall rarely exceeds 40-50%. As before, small (2-5 cm) regenerating colonies of scleractinian Montipora, Porites, Favites, hydroids Millepora, which diversity and abundance, nevertheless, 1.5-2 times dropped, can be met on branched debris of dead corals. The changes also affected the macrobenthos accompanying corals. 20-25 years ago sea urchin Diadema setosum (not less than 5 individuals per sq. m), holothurians Holothuria edulis and H. atra (1-2 ind/m2), sea-stars Linckia laevigata, Culcita novaeguineae, Acantaster planci (0.1-0.2 ind/m2), mollusks Atrina vexillum (up to 0.2 ind/m2), Tridacna crocea (0.5 ind/m2), T. squamosa (0.1 ind/m2), Lambis chiragra, L. scorpius, L. lambis, Trochus niloticus, Cypraea tigris, Mauritia arabica (0.2-0.5 ind/m2) and other invertebrates could be frequently met here. In 2004-2005 only single individuals of Trochus, Atrina, sea urchin Diadema and holothurians H. atra were observed, but the sea star A. planci became very common (0.15 ind/m2).
Erosive consequences of urban development along the coastline, and intensification of mariculture farms in multiple land and island bays greatly increase sedimentation flows and eutrophication of waters of Wan Phong and Nha Trang Bays [21,22]. Connection between sedimentation growth and reduction of species diversity of corals, degree of substratum covering by corals, low growth rates shown in many works [23-25]. Moreover, the increase of the degree of substratum covering by macrophytes observed under conditions like that . Crude sewage and wastes from mariculture farms usually bring nutrient subsidy and toxic materials in water depth and bottom sediments. The increase in the number of fertilizers and pharmaceuticals near reefs increases the content of chlorofyll. This in turn leads to increased levels of nutrients and turbidity is the major causes of the significant changes of corals near the coast .
Differences found in changes of coral communities on island reefs, outlying inhabited localities and aquaculture areas (Den, Mun), and on reefs exposed to intensive anthropogenic press (Mju, Ong et al.) serve as a striking example of differentiated anthropogenic impact. Species diversity index of scleractinian is more than 2.5 times higher on remote and relatively clean reefs in comparison with that of the reefs exposed to the intensive anthropogenic effect (Figures 5 and 6). Reefs of islands, similar to Mju Island, are located in the immediate vicinity to the city and port of Nha Trang. Crowded settlements and tourist complexes are located on its coasts, and multiple mariculture farms operate in its bays. Islands of Mun Island type are farther from the city, and their reefs situated in the reserved protected zone, where there is no population or it consists of not numerous representatives of guards and reserve administration. Water clarity near Mju Island and water exchange intensity over coral reefs here is 1.48 times lower than near Mun Island. At the same time, sedimentation flow is 1.3 times greater. Great degree of anthropogenic influence causes growth of eutrophication of waters, surrounding Mju Island, and intensification of substratum silting [28,29]. Because of these changes, the degree of substratum covering by corals reduces, and the area of its covering by macrophytes increases. Reduction of diversity of reef- building corals and accompanying mass macrobenthos species takes place. Replacement of Acropora, dominated earlier on Mju Island reefs, by fine-branched Montipora, having greater total surface area of a colony, can be considered as a possible consequence of high content of dredge, deposited in this area (1.3 times higher than in other places).
Figure 5: Variation in the substrate coverage; (A) and the species diversity index (B) in reef communities of Tho Chau Island. 1, coastal polyspecies community; 2, Acropora nobilis + A. microphthalma facies; 3, Acropora + Diploastrea community; 4, reef slope community; 5, Junceella fragilis + Diaseris distorta community.
Repeated studies of reef open part of the South China Sea and the Gulf of Thailand to notice that the reef with moderate or low anthropogenic impact, and even more so in places where environmental measures are satisfactory and remain even with optimal conditions for existence of reef communities. These reefs are characterized by a high degree of substrate coverage of living corals, are rich in species of hermatypic corals and associated fauna, including fish. An example are the reefs of Hon Den, Mun Islands at the Khanh Hoa province under State protection, reefs Bath Longvi island and the Spratly archipelago [30-32] as evidenced by the results of the study, the ecosystem of Con Dao Islands, is not subject to any explicit human impacts, including mariculture farms.
It is shown that fringing reefs of Con Dao and Thu islands open part of the South China Sea on the morphology, the degree of development of coral structures, the qualitative and quantitative composition of corals are comparable to other reefs of South Vietnam [16,33]. 256-365 species of scleractinian found on these reefs, 80 – 83% of the species occur on other reefs of Vietnam, we studied. Along with developed reef, with a clear physiographic zoning, to the East and North of the of Con Dao and Thu Islands built around the middle stage of development characterized by massive forms of corals development of macrophytes, and mild zoning. The same features and similar zoning with each zone communities of algae and corals, wide development bioherms with domination of Acropora palifera, Porites cylindrica, Millepora dichotoma and Heliopora coerulea we saw near the of Coetivy Island (Seychelles). A similar feature other Seychelles reefs bring Rosen  and Latypov . Thus, the results of earlier studies showed that the island reefs of the Gulf of Thailand and South Vietnam characterize as an obvious commonality with other reefs Indo-Pacific and obvious traits of identities that require detailed study and conservation. These areas of Vietnam into the active zone, fisheries, tourism and intensive construction, therefore, to determine the reasons for the negative and positive change on reefs need repeated studies previously studied coral reefs. Such studies are relevant also in the light of the extensive planetary changes in reef communities, taking place under the influence of natural climatic processes [30,32].
In many works, which are not necessary to cited here, they analyze the level of physical and biological effects, resulting in disruption of species composition and structure of coral communities. At that, it universally recognized that the state of coral reefs is noticeably becoming worse on the global level. At present, it is essentially to know what we are trying to preserve diversity of corals on a certain reef, its fish resources or ecosystem as a whole. Changes may take place on the level of an individual, population, ecosystem and landscape. Impacts affecting these levels can be short-term and long-term. Short-term impacts can shadow long-term ones. Only long-term monitoring, including single, short-term and long-term natural and anthropogenic impacts, will allow us to estimate stability of coral reef communities and to identify the tendency and reasons of changes. At the same time, it is necessary to observe strictly technologies of marine objects cultivation in the areas of aquaculture, to expand areas and number of preserved and protected zones together with artificial restoration of biological diversity of reef-building scleractinian on reefs. All that will allow us not only to preserve and restore, but also to use rationally the unique ecosystem of Vietnamese reefs.
The author is grateful to A.G. Goloseev, N.I. Selin, Chan Din Nam, Dao Tan Ho for assistance during the studies of reef communities and identification of flora and fauna.
- Serene R (1937) Inventaire des invertébrésmarins de l’Indochine. InstOcéanogrIndochine 30: 3-83.
- Dawydoff C (1952) Contribution et l’étude des Invertébrés de la faune marine benthique del’Indochina. Bull Biol France Belg 37: 1-158.
- LatypovYuYa (1982) Composition and distribution of scleractinians on reefs of PhuKhanh Province (South Vietnam) BiolMorya 8: 5-12.
- LatypovYuYa (2003) Reef-building corals and reefs of Vietnam: 1. The Gulf of Thailand, Russ. J Mar Biol 29: S22-S33.
- Ken LV (1991) The stony corals in the seas of Vietnam, Marine environment and Resources (1986–1990) Hanoi: Sci Tech Publ House 127-135.
- LatypovYuYa (1986) Coral communities of the Namsu Islands (Gulf of Siam, South ChinaSea). Mar EcolProgSer 29: 261-270.
- LatypovYuYa (1995) Community structure of scleractinian reefs in the Baitylong Archipelago (South China Sea). Asian Mar Biol 12: 27-37.
- WWF (1994) Vietnam Marine Conservation Southern Survey Team. Survey report on the biodiversity resource utilization and conservation potential of PhuQuoc Islands, KienGiang Province, Gulf of Thailand. Gland Switzerland unpublished report.
- Yet NH (1997) Characteristic species and coral reef structures at Fishermen Dao (Spratly Islands).Res Mar Environ 4: 299-313.
- LatypovYuYa (2008) Species composition and structure of coral community of a platform reef at Bach Long Vi Island in the South China Sea. Russ J Mar Biol 34: 249-253.
- LatypovYuYa, Selin NI (2011) Current Status of Coral Reefs of Islands in the Gulf of Siam and Southern Vietnam Russ. J Mar Biol 37: 255-262.
- LatypovYuYa (2012) Encrusting protected reef Hon Nai in Cam Ranh Bay in the South China Sea. Nat Sci 4: 14-21.
- LatypovYuYa, Selin NI (2012) Changes of reef community near Ku Lao Cham Islands (South China Sea) after Sangshen Typhoon.AmerJ Climate Change 1: 41-47.
- LatypovYuYa (1982) Composition and distribution of scleractinian on the reefs of Phukhanh (Southern Vietnam). Soviet J Mar Biol 6: 5-12.
- LatypovYuYa (1990) Scleractinian corals of Vietnam. Part I. Thamnasteriidae, Astroiidae, Pocilloporidae, Dendrophylliidae. Moscow. Nauka, (In Russian).
- LatypovYuYa (2005) Reef-Building Corals of Vietnam as a Part of the Indo-Pacific Reef Ecosystem. Russian J Mar Biol 31: S34–S40.
- Loya Y, Slobodkin LB (1971) The coral reefs of Eilat (Gulf of Eilat, Red Sea), Symp.ZoolSoc London 28: 117-139.
- Mandaville S (2002) Benthic macro invertebrates in freshwaters–Taxa tolerance values,metrics, and protocols. Project H-1. Nova Scotia. Soil and Water Conservation Society ofMetro Halifax,
- LatypovYuYa (1987) Scleractinian corals of South Vietnam. Soviet J Mar Biol 13: 246-252.
- Vo ST, Hodgson G (1997) Coral reefs of Vietnam. Recruitment limitation and physical forcing. Proc Eight Intern Coral Reef Symp 1: 477-482.
- An NT, Son VD, Thu PM (2000) Tracing sediment transport and bed regime in NhaTrang Bay. Coll Mar Res Works 10: 63-69.
- Huan NB, Hoang Son TP (2000) The characteristics of distribution and change of the seawater temperature and salinity of Cai river and northern part of Nhatrang bay in dry and rainy seasons. Coll Mar Res Works 10: 63-69.
- Cortes J, Risk M-J (1985) A reef under siltation stress. Cahuita, Costa Rica. Bull Mar Sci 36: 339-356.
- Tomascik T, Sander F (1987) Effects of eutrophication on reef corals. II. Structure of scleractinian coral communities on fringing reefs, Barbados, West Indies.MarBiol 94: 53-75.
- Andres N, Witman JD (1995) Trends in community structure on a Jamaican reef. Mar EcolProgrSer 118: 305-310.
- Dai CF (1996) Dynamics of coral communities. In. Turner IM, Diong CH, Lim SSI, NgPKL (ed).Biodiversity and the Dynamics of Ecosystems,DIWERSITAS Western PacificandAsia 1: 247-265.
- Fabricius KE (2006) Effects of irradiance, flow, and colony pigmentation on the temperature micro environment around corals. Implications for coral bleaching? Limn and Oceanogr 51: 30–37.
- Pastorok RA, Bilyard G (1985) Effects of sewage pollution on coral-reef communities. Mar Ecol Prog Ser 21: 175-189.
- Latypov YuYa (2007) Scleractinian Corals of Vietnam. Moscow, Nauka.
- Veron JEN (1995) Corals in space and time. The biogeography and evolution of the Scleractinia. UNSW PRESS.
- Yet NH, Ken LV (1996) Some Data on Species Composition and Distribution of Scleractinian Corals in Ha Long Bay. J Biol (Hanoi) 18: 7-13.
- Latypov YuYa (2008) Species Composition and Structure of Coral Community of a Platform Reef at Bach Long Vi Island in the South China Sea. BiolMorya 34: 293-296.
- LatypovYuYa (2003) Reef-Building Corals and Reefs of Vietnam: 1. The Gulf of Thailand. Russian J Mar Biol 29: S22-S33.
- Rosen BR (1971) Principal features of reef coral ecology in shallow water environments of Mahe, Seychelles. Symp Zool Soc London 28: 163-183.
- Latypov YuYa (2009) Species Composition and Distribution of Scleractinians on the Reefsof the Seychelles Islands. Russian J Mar Biol 35(6): 454-462.
Citation: Latypov YY (2015) New Data on Spatio-temporal Stability and Variability of the Vietnamese Reefs. J Biodivers Biopros Dev 2: 152. Doi: 10.4172/2376-0214.1000152
Copyright: ©2015 Latypov YY. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
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