ABSTRACT

Coral Reef Health in Bali Indonesia has proven to be directly correlated with tourism revenue for the community as well as a dependent source of foods through the fish supply. However, coastal land-based factors and practices have been proven to affect and degrade the coral reef ecosystems and overall health (Edinger, Jompa). High resolution satellite imaging and specific band studies (NDVI, Band 1, 3-D images) surveyed on 2 comparative regions of Bali Indonesia (Permuteran Region & Alas Purwo Peninsula) allows for a comparative study of coral reef degradation, extent, and shape as it relates to the local land development, vegetation densities, and coastal slope in those regions. The results found that regions with low land development, high vegetation densities, and softer sloping coastal characteristics, such as Alas Purwo Peninsula, support more uniform and extending coral reef habitats. Regions with high land development, low vegetation densities, and steeper sloping coasts, such as the Permuteran region, support relatively less uniform, less extensive coral reef systems.

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INTRODUCTION

Despite its diving industry little is known about the state and health of the coral reefs in Bali and few publications exist dealing with reef management. The coral reefs, made of limestone, not only provide food and for local coastal communities but also play an essential role for marine habitat. The large sections of reef along the Bali coastline provide breeding grounds for fish, shelter for marine habitat, protection from coastal erosion, and account for most of the world’s coral species. West Bali, particularly the Pemuteran area, has large areas of shallow reef and calm currents making it a diving and snorkeling paradise as well as an easy target for fishermen.

Although Bali reefs have a high variation in regards to water temperature, substrates, and salinity the reefs have been severely damaged in recent years from destructive fishing techniques. The use of bombs and cyanide to capture dead fish along with the increasing effects of global warming has led to over 80% of the reefs in Bali being damaged in some way. A survey from the Reef Check Foundation Indonesia (RCFI) showed that the highest percent of coral bleaching, around 40%, is occurring in the Pemuteran area.

Corrective measures from various parties are needed to manage the impacts of coral bleaching. Loss of tourism revenue will continue to affect the local economy. “According to economist Dr. Herman Cesar, a severe coral bleaching event in the next 50 years in South East Asia would cause financial losses up to 38.3 Billion from reduced products and services from fisheries and tourism. Also the damage caused to local fish habitats will lead to a decrease in supply of fish for local subsistence.

The economic and ecological threats to Bali local communities will continue to deteriorate so long as the destruction and bleaching of the Coral Reefs continues. “Many studies have shown that healthy reefs are better able to recover from the effects of climate change. The importance of reducing ‘everyday’ threats to coral reefs to ensure their survival in the face of climate change cannot be emphasized highly enough,” Dr Joanne Wilson further noted.

As a primary supporter of food sources and tourism revenue, the Coral Reefs in Bali are of extremely high importance in sustaining a quality of life within the region. In order to further understand the relationship between the health of the coral reef and the activity of the mainland populations, we will study various Satellite images. Through the imaging techniques, we will compare the Permuteran Area of Bali and the Alas Purwo Peninsula of the National Park of Alas Purwo to determine the relations of local anthropogenic factors of the mainland with coral health in the ocean.

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METHODS: STUDY AREA

Study Area: Pemuteran Coral Reef on the Northwest corner of Bali; South East Alas Purwo Peninsula Coral Reef in Alas Purwo National Park near Bali

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METHODS: DATA

Band-1 Analysis

Visible Band-1 Analysis

3-D Visible Band-1 Analysis

NDVI Analysis

Nighlight Analysis

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METHODS: BAND-1 ANALYSIS

The grayscale image of band 1 provides increased penetration of water bodies while also differentiating soil and rock surfaces from vegetation, commonly used for detecting cultural features (Band Combinations).  The Band 1 image was downloaded from the ERTS Satellite of the Landsat Program through NASA.

The two images provided below the Overview Image are Sub-set Band 1 images of 1) the Alas Purwo Peninsula and 2) the Pemuteran Area. The water penetration abilities of band 1 allow for a visual measure of coral reef extension from the mainland. 

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METHODS: VISIBLE + BAND-1 ANALYSIS

The visible Spectrum – Band 1 image was created through the ENVI Program by applying a RGB (visible) spectrum to the Band 1 Image downloaded through the ERTS Satellite of the Landsat Program.

On the terrestrial land, the visible spectrum applied to the Band 1 Image of the study area allows for a differentiated study of soil and rock surfaces from vegetation, commonly used for detecting cultural features such as land development and farming. Dark green indicates regions that contain high vegetation levels, while yellow indicates regions that contain relatively lower vegetation levels.  Finally, magenta and purple indicate the relatively lowest vegetative levels.

In the Ocean, the visible spectrum applied to the Band 1 Image of the study area allows for a visible study of the extent of Coral Reef and the form of the Reef. Light green area’s off the coast indicate area’s where the coral reef is closer to the surface with dark green indicating deeper coral reef.

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METHODS: 3-D VISIBLE BAND-1 IMAGE

The 3-D – Visible Band 1 Image is created by linking the Visible Spectrum version of Band 1 with Elevation Data provided by the Shuttle Radar Topography Mission (SRTM) to create a 3-D Image of the Blue Band. The 3-D image provides analysis of mountain slopes and mainland run-off channels for the terrestrial lands. The Visible Band 1 data highlights culturally developed regions and coral reef extent, as outlined above.

The Sub-set images of the 3-D images have been focused on 1) the Alas Purwo Peninsula and 2) the Pemuteran Area; the images have also been adjusted off-nadir, allowing for topographic analysis of the study areas, including slope differences of the coast. 

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METHODS: NDVI ANALYSIS

The Normalized Difference Vegetation Index (NDVI) data provides a numerical value to the relative amount of live green vegetation. Through the ENVI Program, we created the NDVI Image with bands 3 and 4 (Red and IR) from the ERTS Satellite of the Landsat Program images by using the formula of (NIR-Red/NIR+Red). The brightness of the purple shade refers to the higher value of the vegetative growth.

The two NDVI Sub-Set images provided below the Overview Area provide a comparative study of the density of vegetative canopies on the main lands of 1) the Alas Purwo Peninsula and 2) the Pemuteran Area.

Below the NDVI Sub-set images, a density slice study of the respective sub-sets provides color differentiated digital data. The data is enhanced through density slicing and is more easily interpreted through the slicing of the NDVI bands into ranges. Each range is associated with a provided color spectrum. In our model, green indicates area’s of the highest NDVI produced density of vegetative growth, followed by red, and finally yellow containing the least relative vegetation.

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METHODS: NIGHT LIGHT IMAGE

The Nightlight Image was produced as a sub-set of the Global Defense Meteorological Satellite Program (DMSP) run by the National Oceanic and Atmospheric Administration. The image provides for an analysis of light pollution in the study area’s, with white areas indicating light emissions, and dark areas indicating little to no light.

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RESULTS: QUESTIONS

What do we see from the satellite imagery? What can we say about the mainland adjacent to the coral reef, based on our satellite images? How does mainland activity effect Coral Reef Health?

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