CENTRAL AFRICAN REGIONAL PROGRAM FOR THE ENVIRONMENT |
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Issue Brief #13 |
#13 Monitoring Forest Cover in Central Africa
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This brief was written by the University of Maryland. For more information on forest mapping activities contact Nadine Laporte, email: nlaporte@geog.umd.edu; Chris Justice, email: justice@hermes.geog.umd.edu.
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Key Concepts
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The Congo Basin contains the second largest continuous rainforest in the world. It includes the some of the highest biodiversity of Africa and sustains more than 20 million people (Table 1), most of whom depend on natural resources for their livelihoods, including agriculture, non-timber forest products as a source of food, medicines and income, and timber. Collection of, and public access to national and regional scale information on forest types, distribution and rates of conversion is a necessary but insufficient step to greater equity in forest management decision making and benefit sharing. In the 1980's, after publication of the deforestation rates in the Amazon basin, the government of Brazil and the World Bank were accused of promoting deforestation by building new roads and giving away large areas of forestland to settlers. As a result a new policy was adopted that settlers would have to retain at least 40% of their land in forest. Similarly, in Indonesia, forest monitoring proved that, contrary to government assertion, most of the forest burning was not caused by smallholders, but by politically influential industrial plantations. Monitoring does not always lead to new forest policies, but is a fundamental step in managing natural resources.
Africa's national forest agencies have been under-funded for long time and have had to rely on collaboration with foreign institutions to overcome the lack of up to date information on forest cover and forest conversion. The combination of high population growth and increased world demand for forest products necessitate the development and implementation of innovative and sustainable forest management plans that will help ensure that forest uses benefit the majority and do not compromise access to these benefits in the future.
What is monitored must be determined by the demand for environmental information. For example, local communities might be interested in tracking the expansion of immigrant farmers into their traditional territories, national forest agencies may want to know where timber companies are logging particularly if they are taxed based on their concession area, protected area managers may be keen to monitor the location and size of gold and diamond mining camps, biologists may want to track tree mortality and regeneration rates under different management regimes, and global climate modelers would like to monitor rates of carbon accumulation and emissions within forests of different types.
"The goal is to provide timely and reliable information on forest composition, condition, and extent, as a basis for informed decision making."
Supplying forest information in the absence of demand is, however, unlikely to result in changes in forest policies and practices. After five years, the logging company that collaborated on the API-Dimako project was uninterested in making use of the vast supply of research results for improved forest management, because more efficient harvesting offered it no competitive advantage. Similarly, the influence of FORAFRI and REIMP two other donor projects, on forest management by making environmental information more available to governments, has yet to be assessed.
That said, increasing public rather than simply public-sector access to information may empower latent constituencies for forest policy reform, and consequently build demand for more and better forest information. Providing nascent civil society institutions with environmental information with which to lobby government for changes in forest policies and practices may be a more effective use of environmental information than providing it directly to uninterested ministries.
Different characteristics of forests can be monitored at different spatial and temporal scales to address different management concerns. Moreover, information can be gathered both physically by people on the ground, or remotely using cameras and other sensors flown on airplanes and satellites. To monitor compliance with forestry laws, information on the location and extent of logging may only need to be gathered once a year within and bordering a concession, over an area of typically less than 200,000 ha, and could be accomplished either by forestry staff visiting the concession, or by using remote sensing to record the location of new logging roads and the number of new canopy gaps associated with felled trees. To establish a sustainable forest management plan information on tree fruiting times, seedling mortality, recruitment, and mortality would have to collected monthly by field staff, over an area of at least 10 ha. Agricultural expansion into forested areas, and forest fragmentation by roads, could be monitored on a yearly basis using satellite imagery over relatively vast areas.
Field-based monitoring is, not surprisingly, more expensive than using remote sensing data. In general monitoring costs increase with spatial scale, level of detail and accuracy, and the frequency of data collection (Table 2).
Table 1: Central African Statistics on Forests and Population |
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| Population1 (millions) |
Population Density |
Deforestation Rate 80-90s2 |
Forest Cover4 (%) |
Agriculture and Fallow4 (%) |
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| Cameroon | 12.80 | 27.5 | 0.6 | 37.0 | 14.0 |
| Central African Republic (CAR) | 3.20 | 5.2 | 0.4 | 10.0 | 10.0 |
| Dem. Rep. of Congo (DRC) | 42.60 | 18.3 | 0.6 0.43 | 48.0 | 4.0 |
| Equatorial Guinea | 0.39 | 15.6 | 0.4 | 65.0 | 23.0 |
| Gabon | 1.30 | 4.9 | 0.6 | 80.0 | 9.0 |
| Rep. of Congo | 2.50 | 7.3 | 0.2 | 66.0 | 11.0 |
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Traditionally Africa's national forest services have provided inventories and monitored forests for timber exploitation using expensive, time consuming, and intermittent aerial surveys. High cost of aerial photography and photo-interpretation limited these surveys to only small areas. In most countries, lack of demand, high cost, and insufficient technical staff and operating budgets, has meant that forest assessments have not been updated for decades, if at all.
Remote sensing imagery provides Central African nations with an alternative, timely and cost-effective approach to monitoring changes in forest cover at multiple scales. Satellite imagery and aerial-videography are now an essential part of most large area forest monitoring systems. However, remote sensing images are not a substitute for field-based data collection, which is essential for accurate image interpretation and to provide the necessary data on forest characteristics that are undetectable by air- and space-borne sensors.
Given the immense area covered by Africa's rainforests (approximately 1.8 million km2), and their relative inaccessibility, a combination of remotely sensed data used and targeted field-based forest inventories will produce the most accurate and timely estimates of forest cover type, relative distribution and rates of change, at local to regional scales.
At the regional level, optical image data from NOAA-AVHRR sensors, and the new MODIS and SPOT VEGETATION instruments are the primary systems for gross differentiation between forest, savanna and agriculture. These systems have neither the spatial nor spectral resolution to discriminate multiple forest types.
At the national or local level, Landsat or SPOT imagery can provided finer scale information on forest type distribution and agriculture expansion.
Optical sensors like the Landsat Enhanced Thematic Mapper offer good spatial coverage for most of the Democratic Republic of Congo and Central African Republic. However, wall-to-wall mapping of Cameroon, Gabon and the Republic of Congo is difficult because of perennial cloud cover. Radar systems such as JERS and Radarsat are not affected by clouds, and are useful for determining the extent of forest and non-forest landscapes where topographic relief is not substantial (<200m). Radar imagery is, however, unable to differentiate between high woody biomass old-growth or unlogged forests from degraded lower biomass forest types.
International efforts are underway to improve operational forest monitoring as part of the Global Terrestrial Observing System. At the first Global Forest Observation of Forest Cover (GOFC, 2000) workshop held in central Africa (February 2000 in Libreville, Gabon), several issues limiting the development of operational forest monitoring systems were identified by national forest services and their international partners. These included: (1) lack of human and financial resources; (2) poor access to data and information; (3) poor Internet access; and (4) lack of training facilities and opportunities.
In the Central African region, as part of the international GOFC initiative, new remote sensing tools and methods will be tested for local and regional scale monitoring. In addition, future workshops, technical exchanges, and collaborative research activities will continue to strengthen national capacity for forest monitoring. The latter is particularly important given the paucity of technical expertise in the region.
These activities will foster the growing collaboration between national forest services, universities, conservation organizations and the logging private sector. For example the utility of new high resolution IKONOS imagery (at 1 and 4m resolution) will be evaluated for forest concession management at very fine scales. In Gabon IKONOS data will be tested for mapping recolonization of Okoumé in savanna areas. This tree species is important to the nation economy as it represents more than 70% of log exports. Landsat imagery will also be tested for developing a monitoring system for logging activities in Cameroon, Gabon and the Republic of Congo. The FAO Africover Project will be extended into Central Africa strengthening capacity for national forest mapping and monitoring and building on the satellite data sets developed by CARPE, NASA and the ECE.
To improve the access to spatial information for forest monitoring, recent imagery from Landsat 7 will be made available on CDs by CARPE for nationals forest services, conservation organizations and the CARPE - GOFC network. Also, the NASA Landsat Pathfinder archive will continue to be available via the Internet and CDs. (http://glcf.umiacs.umd.edu; http://www.bsrsi.msu.edu/trfic/).

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Legend 1: Tracking logging with digital videographies. |

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Legend 2: Tracking logging with digital Landsat TM imagery. |

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Legend 3: MODIS image of Bandudu province. |
Figure 1: Extent of the Rainforest from TREES and CARPE (1990s) |
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Table 2: Tools for Monitoring Changes in Forest State |
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| Scale | Data Source |
Forest Attributes |
Spatial Resolution |
Temporal Frequency |
Mapping Scale |
Monitoring Cost |
| REGIONAL | AVHRR | Forest/Non forest | ||||
| SPOT vegetation | Net primary productivity | |||||
| Seasonality | ||||||
| Forest disturbances: | 1 km2 | daily | >1/500,000 | Low | ||
| Agriculture | ||||||
| NATIONAL | Landsat | Forest types | ||||
| SPOT | ||||||
| Forest disturbances: | 100 m2 to 900 m2 |
15-20 days | > 1/50,000 | Low to high | ||
| Agriculture | ||||||
| Logging roads | ||||||
| Plantations | ||||||
| LOCAL | IKONOS | Tree species | ||||
| Aerial-videography | Human population growth and movements | 1 m2 to 16 m2 |
User defined | > 1/500 | High | |
| Forest disturbances: | ||||||
| Agriculture | ||||||
| Logging roads | ||||||
| Plantations | ||||||
| Tree gaps | ||||||
| Field staff | Species composition | <1m2 | User defined | > 1/500 | Very high | |
| Harvest rates | ||||||
| Level of degradation | ||||||
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Note: Due to cloud coverage data availability differs from data temporal frequency |
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Laporte N., C. Justice, J. Kendall. 1995. "Mapping the dense humid forest of Zaire and Cameroon using AVHRR satellite data." International Journal of Remote Sensing 16(6):1127-1145.
Mayaux, P., E. F. Lambin. 1995. "Estimation of tropical forest area from coarse spatial resolution data: A two-step correction function for proportional errors due to spatial aggregation." Remote Sensing of Environment 53:1-16.
Skole, D. S., C. O. Justice, A. Janetos, and J. R. G. Townshend. 1997. "A land cover change monitoring program: A strategy for international effort." Mitigation and Adaptation Strategies for Global Change 2(2-3):157-175. The Netherlands: Kluwer Academic Publishers.
Wilkie D., N. Laporte N. 2001. "Forest area and deforestation in Central Africa: Current knowledge and future directions." African Rainforest Ecology and Conservation, ed. W. Weber, A. Vedder, S. Morland, and L. White. New Haven: Yale University Press.
Launched in 1995, the Central African Regional Program for the Environment (CARPE) engages African NGOs, research and educational organizations, private-sector consultants, and government agencies in evaluating threats to forest integrity in the Congo Basin and in identifying opportunities to sustainably manage the regions vast forests for the benefit of Africans and the world. CARPEs members are helping to provide African decision makers with the information they will need to make well-informed choices about forest use in the future. BSP has assumed the role of "air traffic controller" for CARPEs African partners. Participating countries include Burundi, Cameroon, Central African Republic, Democratic Republic of Congo, Equatorial Guinea, Gabon, Republic of Congo, Rwanda, and São Tomé e Principe.
Web site:
http://carpe.umd.edu
The Biodiversity Support Program (BSP) is a consortium of World Wildlife Fund, The Nature Conservancy, and World Resources Institute, funded by the United States Agency for International Development (USAID). This publication was made possible through support provided to BSP by the Africa Bureau of USAID, under the terms of Cooperative Agreement Number AOT-A-00-99-00228-00. The opinions expressed herein are those of the authors and do not necessarily reflect the views of USAID.

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For the Congo Basin Information Series © 2001 by WWF. WWF authorizes, without its prior permission, reproduction for educational and other noncommercial purposes of the portions of this publication to which it holds the copyright. However, it does request advance written notification and appropriate acknowledgment. WWF does not require payment for the noncommercial use of its published works. Photographs used by permission of the photographers (NASA and University of Maryland). For information on copyright in the text of this Issue Brief, contact the first writer identified at the beginning of this document.