Provides a detailed analysis of threats to coral reefs across Southeast Asia and provides an economic valuation of what will be lost if these threats -- destructive fishing, overfishing, marine-based and inland pollution, coastal development -- continue.
People have coexisted with coral reef ecosystems in Southeast Asia for thousands of years. With more than 350 million people living within 50 km of the coast, coral reefs are important not only in local communities’ cultures, but are also critical to the economic health of these nations.
Despite their worth, coral reefs in Southeast Asia face unprecedented threat levels from human activities. The population explosion during the last 50 years is driving many of the current pressures and is creating elevated, often unsustainable demand on both the terrestrial and marine resources of the region. These pressures are jeopardizing the incredible value of coral reefs, whose loss would have significant economic impacts for the region.
Key findings of the report include:
Biological endowment. Southeast Asia contains nearly 100,000 square kilometers of coral reefs, almost 34 percent of the world total. With over 600 of the almost 800 reef-building coral species, these reefs have the highest levels of marine biodiversity on earth. Southeast Asia is also the global center of biodiversity for coral reef fish, mollusks, and crustaceans. The region also contains 51 of the world’s 70 mangrove species and 23 of the 50 seagrass species.
The economic value associated with coral reefs in Southeast Asia is substantial. The value of the region’s sustainable coral reef fisheries alone is US$2.4 billion per year. In addition, coral reefs are vital to food security, employment, tourism, pharmaceutical research, and shoreline protection. The coral reefs of Indonesia and the Philippines provide annual economic benefits estimated at US$1.6 billion and US$1.1 billion per year, respectively.
Threats to reefs. The heavy reliance on marine resources across Southeast Asia has resulted in the overexploitation and degradation of many coral reefs, particularly those near major population centers. The main threats include overfishing, destructive fishing practices, and sedimentation and pollution from land-based sources. Human activities now threaten an estimated 88 percent of Southeast Asia’s coral reefs, jeopardizing their biological and economic value to society. For 50 percent of these reefs, the level of threat is “high” or “very high.” Only 12 percent of reefs are at low risk.
Effective management is key to maintaining coastal resources, but, is inadequate across much of the region. Some 646 marine protected areas (MPAs) cover an estimated 8 percent of the coral reefs. Of the 332 MPAs whose management effectiveness could be determined, only 14 percent were rated as effectively managed, 48 percent have partially effective management, and 38 percent have inadequate management.
Lack of information. Despite widespread recognition that coral reefs are severely threatened, information about the status and nature of the threats to specific reef areas is limited. This lack of information inhibits effective decisionmaking concerning coastal resources. The Reefs at Risk project was developed to address this deficiency by creating standardized indicators that raise awareness about threats to coral reefs and to highlight the linkages between human activity and coral reef condition.
Menteri Kelautan dan Perikanan Indonesia Kata Pengantar
Puji syukur ke hadirat Tuhan Yang Maha Esa atas berkat dan bimbinganNya sehingga World Research Institute (WRI) dapat menerbitkan buku Reefs at Risk Southeast Asia-Summary for Indonesia yang kemudian diterjemahkan dalam bahasa Indonesia dengan judul Terumbu Karang yang Terancam di Asia Tenggara-Ringkasan untuk Indonesia.
Sebagai negara kepulauan terbesar dan secara geografis terletak di antara Samudera Pasifik dan Samudera Hindia, keanekaragaman hayati laut Indonesia tak tehitung jumlahnya. Terumbu karang Indonesia sangat beraneka ragam dan memegang peranan yang sangat penting dalam menjaga keseimbangan lingkungan dan menyumbangkan stabilitas fisik pada garis pantai tetangga sekitarnya. Oleh karena itu harus dilindungi dan dikembangkan secara terus menerus baik untuk kepentingan generasi sekarang maupun generasi mendatang.
Terumbu karang sangat mudah terpengaruh oleh kondisi lingkungan sekitarnya baik secara fisik juga biologis. Akibat kombinasi dampak negatif langsung dan tidak langsung pada terumbu karang Indonesia, sebagian besar terumbu karang di wilayah Indonesia saat ini sudah mengalami kerusakan yang sangat parah. Bagaimanapun juga, tekanan terhadap keberadaan terumbu karang paling banyak diakibatkan oleh kegiatan manusia, sehingga perlu dilakukan langkah-langkah pencegahan. Peningkatan kegiatan manusia sepanjang garis pantai semakin memperparah kondisi terumbu karang.
Oleh karena itu merupakan kebutuhan mendesak untuk menerapkan konservasi dan rencana-rencana pengelolaan yang baik untuk melindungi terumbu karang dari kerusakan yang semakin parah. Langkah dan kebijakan yang perlu dilakukan untuk mengurangi ancaman terhadap terumbu karang di Indonesia adalah dengan meningkatkan kesadaran masyarakat terhadap perlunya menjaga kelestarian terumbu karang dan mengadakan perencanaan pengelolaan wilayah pesisir yang baik dengan cara mengidentifikasi tingkat kerawanan dari terumbu karang dan meningkatkan pengelolaan yang berkesinambungan.
Saya berharap dengan terbitnya buku Terumbu Karang yang Terancam di Asia Tenggara-Ringkasan untuk Indonesia ini menjadi referensi yang baik bagi pemeliharaan dan pengembangan terumbu karang yang berkelanjutan di Asia Tenggara dan dapat meningkatkan kesadaran serta keterlibatan semua pihak dalam menjaga kelestarian terumbu karang di Indonesia.
Menteri Kelautan dan Perikanan Republik Indonesia
Reefs at Risk in Southeast Asia CD
The Reefs at Risk in Southeast Asia (RRSEA) Data CD contains the range of data assembled and model results developed under the RRSEA project. Included on this CD are over fifty spatial data sets reflecting physical, environmental and socioeconomic variables for Southeast Asia as well as the results of the modeling of human pressure on coral reefs for the region. The CD also provides full technical notes on the threat modeling method and the Reefs at Risk report in .PDF format.
Spatial data sets are best viewed using ESRI ArcView software, but can also be viewed using ESRI ArcExplorer, a public domain software provided on this CD.
To order a copy of this CD, contact email@example.com.
GIS Data Sets
Point Data Sets (ZIP archive, 24.7 Mb) reflecting coral reef locations classified by estimated threat. This option provides six point data sets, a polygon data set of watershed boundaries (with associated erosion estimates) and a polygon data set reflecting country boundaries. (The six threat estimates are for the individual threats - coastal development, marine-based pollution, overfishing, destructive fishing, and sediment and pollution from upland sources, in addition to integrated threat -- the Reefs at Risk threat index.) The archive also includes an ArcView project file which requires ESRI's ArcView software.
GRID Data Sets (ZIP archive, 23.1 Mb) reflecting threat estimates, and coral reef locations classified by threat estimate. This option provides 17 grid data sets, a polygon data set of watershed boundaries (with associated erosion estimates) and a polygon data set reflecting country boundaries. The grid data sets include both a threat surface (a threat estimate for all areas) and reef locations classified by the threat estimate for each of the threats considered. These are coastal development, marine-based pollution, overfishing, destructive fishing, and sediment and pollution from upland sources, in addition to integrated threat - the Reefs at Risk threat index. The archive also includes an ArcView project file which requires ESRI's ArcView software and Spatial Analyst 2.0 extension.
The Reefs at Risk model
The Reefs at Risk in Southeast Asia (RRSEA) project includes an area in Southeast Asia approximately bounded by 90 degrees E and 142 degrees E longitude, and 30 degrees N and 11 degrees S latitude. Data were integrated and the analysis performed in an equal area projection (Lambert Equal Area Azimuthal 126,6) at a 1,000 meter (1 kilometer) resolution.
Input data sets and the model method have been extensively reviewed and significantly revised based on input from project partners and at two regional workshops (the RRSEA workshop, April 2000 in Quezon City, Philippines, and the International Coral Reef Symposium (ICRS), October 2000 in Bali, Indonesia).
The model groups threats into five main categories: coastal development, marine-based pollution, overfishing, destructive fishing, and sedimentation from inland sources. Several component sources of potential degradation were identified for each threat category. For example, cities, settlements, airports, mines, and tourist resorts were identified as the primary elements contributing to degradation of coral reefs from coastal development. Once components were identified, they were then converted into a threat estimate using distance-based rules. For three threat categories – coastal development, marine-based pollution, and pollution and sedimentation from inland sources – this “raw” threat estimate was adjusted based upon an indicator of the natural vulnerability of the area to pollution and sedimentation. In addition, three “raw” threat estimates – overfishing, destructive fishing, and coastal development – were adjusted to account for the management effectiveness of the area. The adjustment factors were applied only to those threats for which the adjustments were considered relevant. The five adjusted threat estimates were then combined into an integrated estimate of threat from human activity. A 1-km resolution grid reflecting coral reef locations was overlaid with the integrated threat estimate to produce the Reefs at Risk Index - coral reefs rated by estimated threat from human activities.
The modeling was done at WRI using an iterative approach with extensive input from project partners. Figure 1 provides an overview of the model. The following sections describe the modeling and data sources in detail.
Coral reef locations
The United Nations Environment Programme-World Conservation Monitoring Center (UNEP-WCMC) provided a base data set reflecting coral reefs locations for Southeast Asia. These data were revised substantially during the RRSEA project based upon input and data from project partners.
This indicator is designed to account for differences in how the physical oceanography of a reef contributes to varied responses to pollutants, such as local flushing rates and bathymetry. The model applies natural vulnerability as an adjustment factor in RRSEA’s analysis of threat from coastal development, marine-based pollution, and inland pollution and sedimentation. The natural vulnerability indicator is based upon (in order of importance) the degree of enclosure or embayment, fetch, depth of water surrounding reef, and tidal range. Each component of this layer was developed as a four-class ranked indicator, with lower numbers indicating lower vulnerability.
a) Embayments were developed at WRI using ArcWorld (ESRI, 1992) coastline (1:3 million) as the base. The four classes for the data set on embayments were defined as follows: (1) open water, (2) slightly enclosed, (3) semi-enclosed, and (4) enclosed.
b) A data layer reflecting fetch, which is defined as the distance wind blows across water, was developed at WRI with the collaboration of the University of the Philippines, Marine Science Institute (UP/MSI). ArcWorld (ESRI, 1992) coastline was used as a base. Four classes of fetch were identified: (1) areas exposed to open ocean, (2) areas open to large seas (e.g., South China Sea, Coral Sea), (3) areas open to smaller seas (e.g., Celebes Sea), and (4) areas mostly enclosed.
c) The bathymetry data set is based on 3.7-km resolution TOPEX data (Smith and Sandwell, 1997). TOPEX data were initially resampled to 1-km resolution, and a neighborhood statistic (maximum) for a 3-cell radius was taken. This manipulation results in a data set of a resolution comparable to the original data but adjusted by the maximum depth within a 4-km distance. The four depth classes are: (1) 4-10 meters, (2) 11-40 meters, (3) 41-100 meters, and 4) more than 100 meters.
d) The most complete data set reflecting tidal range for the region comes from the Land-Ocean Interaction in the Coastal Zone (LOICZ, 1998) program. Although this data set is at a coarser resolution than other data layers, regridded at 30 km, it appears to be the best available data source for the region. Tidal range data were classified in four categories reflecting decreasing mean tidal range: (1) greater than 5 meters, (2) 2-5 meters, (3) 50 cm-2 m, and (4) less than 50 cm.
A simple weighting scheme was used in which subsequent factors are given only one half the weight of the previous variable, reflecting decreasing relative importance. The four components were integrated as follows:
The resulting index was assigned to four categories of vulnerability, as follows: (1) low (15-19), (2) medium (20-30), (3) high (31-30), and (4) very high (40-60).
Management effectiveness adjustment
Effective protection and management of coastal resources are important factors in reducing human impacts to coral reefs, increasing awareness, and promoting coral reef health. Using a UNEP-WCMC data set on marine protected areas, the project worked with its partners to improve the data set on MPAs and to develop a preliminary indicator of management effectiveness for some protected areas. The evaluation used staff size, MPA resources, and existence of a management plan as criteria. Areas were classified as having good, partially, or inadequate management effectiveness.
The adjustment for management effectiveness was applied to the analysis of threat from coastal development, overfishing, and destructive fishing. Areas classified as having good management were reduced by a full grade of threat estimate (from high to medium or medium to low, for example). Areas with partial management effectiveness were adjusted downward by one half grade (high to medium/high, for example). The half-grade adjustments are important when the threats are combined, because when cumulative threats are considered, the adjustments can result in the elevation of a threat category.