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Deforestation of TRF a case study of Madagascar

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					Deforestation of Tropical Rainforests - A Case Study of Madagascar

Abstract
In Madagascar, one of the world’s poorest countries, pressures on tropical
rainforests and other ecosystems are accelerating and having a dramatic impact on
Madagascar’s biodiversity, much of which is not found anywhere else in the world.
There have been limited attempts to conserve this great ecological treasure.

Introduction
Figure 1 World map – Madagascar




Considered a ‘megadiversity’ country, Madagascar is among the world's most
biologically diverse places, with incredibly high levels of endemic plants and
animals.

Figure 2 Vegetation in rainforest areas is dense, diverse and highly specialised




Figure 3 Madagascar’s endemic species
 Known    Endemic Known         Endemic             Known higher     Endemic
 mammal mammal bird             bird species        plant species    higher plant
 species species     species                                         species
 105      84         202        104                 9000             6500
Madagascar has been described as a living laboratory of evolution. More than 150
million years ago, Madagascar split from Africa creating the world's fourth largest
island. Madagascar is an island continent and as such has evolved a range of plants
and animals adapted to its own conditions. Much of Madagascar’s flora and fauna is
endemic – 98 per cent of Madagascar's land mammals, 92 per cent of its reptiles,
68 per cent of its plants and 41 per cent of its breeding bird species do not exist
anywhere else. Madagascar is home to all of the world's lemurs (primate species),
all of which are endangered, and two-thirds of the world's chameleons. Plant
species include orchids, pitcher plants and the Madagascan rosy periwinkle (which
contains the most effective known treatment for childhood leukaemia).

However, large-scale deforestation has taken place since the 1970s and less than
10 per cent of the island's original forest-cover remains. Over 300 species of its
plants and animals are threatened with extinction.




Figure 4 Levels of endemicism in Madagascar




Deforestation in Madagascar
Since 1896 when Madagascar became a French colony, the Malagasy forests have
been rapidly depleted.
Figure 5 Remaining primary vegetation




Figure 6 Loss of forest cover




Logging has occurred for:
     shifting cultivation
     grazing
     fuel wood gathering
     economic development
     cattle ranching and
     mining.

Many forests were destroyed in the search for precious woods such as ebony and
rosewood. Other forest products such as raffia, beeswax, honey, lichens, and
camphor were gathered for export. In addition to crops, the construction of railroads
and their operation relied heavily on timber, intensifying the demand for wood.

Until 1950, most deforestation was done by farmers on a very small scale.
However, since 1950, deforestation has increased dramatically. Owing to the
extreme debt incurred by the Malagasy government, the country is exploiting its
wood resources to pay off money owed to northern countries. The extent of the
eastern rainforests at colonisation was 11.2ha. Only 7.6 million ha remained by
1950. By 1985 the eastern rainforests of Madagascar covered only 3.8 million ha.
Thus, in 1985, only 50 per cent of the rainforests that existed in 1950 still remained,
which is 34 per cent of that which originally existed. This amounts to an average
rate of clearance of 111,000ha (1.5 per cent) per year between 1950 and 1985.

Estimates of the extent of the remaining eastern rainforests have ranged from 2.5 to
6.9 million ha. In addition, it is estimated that approximately 165,000ha of forest are
currently cleared per year. Deforestation costs Madagascar between $100-$300
million per annum in decreased crop yields and the loss of productive forests.
Deforestation in Madagascar is directly related to the introduction of cash cropping.
After Madagascar became a colony in 1896, many people fled to the forests and
survived for years as shifting cultivators. At the same time, the colony's
agricultural production was geared primarily for export. Coffee, rice and beef were of
particular importance. The Central Highlands became the primary irrigated rice-
growing region for both subsistence and export crops. Coffee, which remains the
island's major export crop, was planted on the east coast – the region with the
largest remaining forest cover. Soil erosion rates on coffee plots are nearly double
those of lowland subsistence plots because broad expanses of bare soil under the
coffee bushes are particularly vulnerable to violent storms during the rainy season.
Heavy soil erosion still resulted in subsistence areas as steep slopes were cleared
for this purpose – areas removed from the most fertile land reserved for the cash
crops.

Population trends and the environment

Population growth didn't become a factor in forest degradation in Madagascar until
1940, when vaccines were introduced that lowered the death rate. During the next
40 years the population increased rapidly from 4.2 to 9.2 million. This put a
significant strain on the natural resources and estimates show that 4 million
hectares     of    forests  were    cleared     during   this    40-year  period.

Madagascar’s population is poor and still growing very rapidly. This creates great
pressure on the land to provide for the population. With an average GDI (gross
domestic income) per head of US$870 a year and a foreign debt that nearly equals
its gross national product, the island is ranked amongst the poorest nations in the
world.

The island's average population growth rate ranks among the highest in Africa at
3.03 per cent per year. The population of around 16.5 million is expected to reach 28
million by 2025. Madagascar's exploding population is damaging the economy and
the environment.

Figure 7 Key data for Madagascar
 Population in 2002                   16.47 million
 Crude birth rate                     42.4 per thousand
 Life expectancy                      55.7 years
 Literacy                             Males 88%,Females 73%
 Land use                             Arable 4.4%, Permanent crops 0.9%, Other
                                      94.7%
 Population below the poverty line    70%
 Population growth rate               3.03%
 Crude death rate                     12.15 per thousand
 Total fertility rate                 5.77 children per woman
 GDP per head                     $870
 Source of GDP                    Agriculture 34%, Industry 11%, Services 55%
  Source: CIA World Fact Book, 2003

Much of Madagascar’s population is rural, and farming is having an adverse impact
on the environment. The cattle culture is especially strong in central and southern
Madagascar. Unfortunately, too many cattle on too little land have disastrous effects
on natural habitat. Heavy grazing as well as slash-and-burn agriculture cause severe
erosion even where human populations are comparatively sparse. The soils of
western Madagascar have been degraded to the point where the native dry forests
and thickets seem unable to regenerate. Exotic weeds are invading, leading to a
savanna-like landscape.

However, it is not just farming that is causing problems. In 2003, the world’s largest
mining company, Rio Tinto Zinc, announced plans to mine ilmenite (a mineral used
to make paint and toothpaste) in a 6000ha site near Port Dauphin on the southern
coast. The mining could last for up to 60 years. The company believes it will bring
much needed investment to Madagascar - there are plans for a new port and
breakwater, roads and storage facilities. It will certainly attract migrants, and these
may have a detrimental social impact (Port Dauphin has about 3000 unemployed
young men already) as well as creating negative environmental impacts such as
deforestation to make charcoal.

Protecting the landscape – National Parks in Madagascar

National Parks and reserves were first established by the French colonial
government in Madagascar in the 1920s. Today they account for just 3 per cent of
Madagascar’s land area, and only a small percentage of this land is actively
protected.


Figure 8 National Parks in Madagascar
There are three categories of national park:

      Parc National – where farming, hunting, logging and human habitation are
       prohibited
      Reserve Speciale – special reserves to protect less threatened species.
       People can live in these areas but hunting, farming and logging are banned
      Reserve Naturelle Integral – fully natural reserves where access is permitted
       only for authorised research.

Most parks and reserves are managed by ANGAP (translated as the National
Association for the Management of Protected Area), an NGO established in 1991.
Parks and reserves managed by other organisations, such as WWF, are planned to
be handed over to ANGAP in the near future.

Ranomafana National Park

Ranomafana National Park (RNP) is a large area (435km2) of primary rainforest in
southeastern Madagascar (see Figure 8 for location).

It was established in 1991 following the discovery of a previously unknown primate,
the Golden Bamboo Lemur, in 1986. The Park, on the edge of Madagascar's High
Plateau, is extremely mountainous, with elevations ranging from 600 to 1400m. Until
1986, the steepness of the slopes had preserved parts of the park from exploitation
– one-third of the park had been selectively logged, while the remaining two-thirds is
undisturbed. The range of altitudes allows for many different forest types, from
lowland rainforest to cloud forest and high plateau forest.

Climate

Madagascar’s climate is subtropical, with rainfall averaging 2,300-4,000mm
annually. Monthly rainfall is highest from December to March (400mm) and lowest
from May to October (90mm). Temperatures range between 18-20C, with lowest
and highest recorded temperatures in the area being 7oC and 37oC, respectively.
The growing season is therefore year-round. Sometimes the wet season brings
cyclones, which can have a tremendously destructive impact on the trees of the
forest causing extensive tree blow-downs, flooding and river channel changes.

Soils
Soils at RNP are mostly red clay oxisols, developed from parent rock with
extremely low levels of nutrients. These soils are considered some of the most
naturally infertile in the world, with high iron and aluminium concentrations but little
phosphorus.

Figure 9 Soils in the rainforest are usually red in colour – indicating the presence of
iron oxides
The accumulation of iron and aluminium gives the soil a red colour and in some
cases the concentration of aluminium may form bauxite nodules. The soils are often
deep, due to high rates of chemical weathering, heavily leached, due to the high
rainfall totals, and infertile, since most of the nutrients are held by the plants. Under
sustained hot and wet conditions, fine clay and silicate particles are removed in
suspension, while Nitrogen (N), Calcium (Ca), Magnesium (Mg) and Potassium (K)
are carried away in solution.

Most rainforests have infertile soils but those in Madagascar are worse. This is due
to the combination of high rainfall, high elevations and steep slopes, which, in turn,
is reflected in slow tree growth and lower fruit productivity.

Vegetation and biodiversity

The vegetation in rainforests shows many adaptations, for example

      it is evergreen, enabling it to photosynthesise year round
      it is layered, and the shapes of the crowns vary with the layer, in order to
       receive light
      there are buttress roots to stabilise the trees
      some plants have drip tips to shed water, others have saucer-shaped leaves
       to trap water
      some trees are heliophytes and seek the light; others are sciophytes and
       live in the shade

   Figure 10 Tropical rainforests are a mosaic of species and layers
Figure 11 Light is limited below the canopy




Figure 12 Canopy trees are very tall and their foliage is limited to the tree tops




Rainforests are very productive ecosystems: the Net Primary Productivity
(NPP) is approximately 2200g/m2/yr, and the stored energy, or biomass is
45kg/m2. The ecosystem is diverse, with as many as 200 species of tree per ha,
which includes hardwoods like teak, mahogany and yellow wood. The tropics is
the richest area for biodiversity – tropical forests contain over 50 per cent of the
world’s species in just 7 per cent of the world’s land. They account for 80 per
cent of the world’s insects and 90 per cent of primates.

The biological richness of Ranomafana National Park is extremely high. The
diversity of tree species on 1ha plots at Ranomafana amounts to 105 different
known species. This makes it fall somewhere in the middle, in terms of
rainforests, in between lower elevation rainforests in Colombia, South America,
with 197 species, and lowland rainforests in Gabon, Africa, with 99 species. The
lush vegetation contains most of Madagascar's endemic plant families.
Endangered species include golden bamboo lemur, greater bamboo lemur,
aquatic tenrec, Madagascar Serpent Eagle, and the Madagascar Fish Eagle.
RNP contains most species found in the threatened eastern forest corridor of
Madagascar.

Fauna

 Of the species which have a diversity among the highest in the world are:
 primate species, with 12 species in five families, which are all endemic – the
    Park is home to 12 lemur species, several of which are extremely rare, and
 land-snails.
The park contains over one-third of Madagascar's birds (118 species), rare
carnivores, amphibians and reptiles (68 species) including the world's smallest
chameleon.

   More than 80 per cent of the spider species collected have been unknown to
    science.
   Frogs are distinguished by high species diversity.
   Nine species of chameleon have been recorded.
   There are several species of endemic crayfish in the park, and their closest
    relative may live in Tasmania.

Nutrient cycles
The nutrient cycle in the tropical rainforest is one that is easily disrupted.
Tropical rainforests have been described as ‘deserts covered by trees’. Despite
some of the world’s most luxuriant vegetation, tropical rainforests are found on
some of the world’s least fertile soils. This paradox is explained by the closed
nature of the nutrient cycle. Once the vegetation is removed, nutrients are
quickly removed from the system by intense rainfall creating infertile conditions,
even deserts.

Figure 13 The nutrient cycle




The threats to tropical rainforests

One of the main threats to biodiversity is deforestation. Tropical forests are
being destroyed at a rate of over 11 million ha/year (or 21ha/minute). This is
due to a combination of shifting cultivation, commercial logging, cattle
ranching, plantation farming, road clearance and urban development. However,
there are natural causes of deforestation such as drought, climate change
(which can cause drought), and lightning (the main natural cause).

Areas of greatest plant diversity are in LEDCs where the pressure on the
remaining habitat is greatest. Reduced diversity may eliminate options to use
untapped resources for agriculture, industry and medicine. Currently less than 5
per cent of the world’s rainforests are protected. Scientists argue that each
country should protect at least 10 per cent of their habitat and up to 20 per cent
of key habitats such as rainforests.

The value of rainforests

Figure 14 The value of tropical rainforests
                 Industrial uses               Ecological uses                    Subsistence uses
                 Charcoal                      Watershed protection               Saw logs

                 Flood and landslide           Fodder for agriculture             Gums, resins and
                                                                                  oils
                 Pulpwood                      Soil erosion control               Fuelwood
                                                                                  and charcoal
                 Pit sawing and saw            Climate regulation e.g. CO2        Building poles
                 milling                       and O2 levels
                 Plywood and veneer            Special woods and ashes            Weaving materials
                                                                                  and dyes
                 Industrial chemicals                                             Beekeeping
                 Rearing silkworms                                                Fruit and nuts
                 and protection
                 Medicines
                 Genes for crops
                 Tourism

                Rainforests are important for a number of reasons. They serve as the earth's
                lungs, producing the oxygen we breathe and removing C02 from the
                atmosphere. Two-thirds of all of the world's plant and animal species live only in
                the tropics. The loss of tropical rainforest is the leading cause of the extinction
                of species on a global scale.
                Medicines derived from tropical rainforest plants include:
                 curare (used as a muscle relaxant during surgery)
                 diosgenin (used for birth control pills, arthritis, asthma)
                 quinine (used for malaria, pneumonia) and
                 vincristine/vinblastine (used for Hodgkin's disease, leukaemia and other
                cancers).

                Over 2000 tropical plants have been identified by scientists as having anti-
                carcinogenic properties. Worldwide, the commercial value of medicines based
                on natural products is over US$20 billion a year. However, over 60 per cent of
                the world’s population still depend on traditional medicines and most of these
                are derived from plants.

                Agriculture has benefited from rainforests; for example, tea, coffee, bananas,
                oranges, lemons, peanuts and pineapples all originate from these regions.
                Valuable wood such as teak and mahogany is used to build furniture, while
                lower quality wood is used to make plywood and fibreboard. However, forestry
                has many negative impacts and modern machinery can cut down forested
                land at an alarming rate.

                Figure 15 Potential environmental impacts of forestry
Forestry              Water                Soil                   Landscapes                     Nature and
practise                                                                                         wildlife
Planting              Accumulation of            Accumulation of          Uniform planting -     Plantation of
                      litter from acidifying     litter from acidifying   major changes in       monoculture and
                      tree species - soil        tree species - soil      form, colour and       introduced tree
                      acidification;             acidification            texture arising from   species -
                      groundwater                                         sharp boundaries of    uniformity, loss of
                      acidification                                       forest stands          biodiversity

                      Cultivation of
                      productive water-
                      demanding tree
                      species reducing
                      groundwater
                      availability
Clear felling         Bare land after            Bare land after          Large clearances       If dead or
                      clear felling -water       clear felling -wind      scarred landscapes     decaying wood
                erosion increased       and water erosion                              removed - loss of
                sediment and                                                           plant and animal
                organic matter          Use of vehicles -                              species which
                loads -                 compaction                                     depend on this
                eutrophication,                                                        loss of
                sedimentation           Sudden decrease in                             biodiversity
                                        water demand
                                        following clear
                                        felling -waterlogging
Draining        Lowering of             Oxidation of organic    Drying of land         Lowering of water
                groundwater level       soils - acid-sulphate   causing changes in     table - loss of
                reducing water          formation - soil        plant communities      wet forests and
                availability            acidification           and landscape          wetlands high in
                                                                                       biodiversity
                Oxidation of organic
                soils - soil
                acidification,
                groundwater
                acidification
Weeding,        Use of herbicides -     Increased               Removal of             Removal of
cleaning,       groundwater             frequency of vehicle    greenery -uniformity   understorey, an
thinning        pollution               use -erosion and                               important habitat
                                        compaction                                     for many species
                                                                                       - loss of
                                                                                       biodiversity
Pesticide and   Leaching of applied     Fertilisation in        Changes in plant       Release of
fertiliser      substances -            waterlogged             communities and        chemical
application     groundwater             conditions -            hence landscape        pesticides -
                pollution               denitrification                                poisoning of non-
                                        greenhouse gas                                 target species
                                        emission -
                                        contribution to                                Fertilisers
                                        climate change                                 applications -
                                                                                       changes in plant
                                                                                       communities
Heavy           Soil erosion -          Increased                                      Increased
machinery use   increased sediment      frequency of vehicle                           frequency of
                load in surface         use - soil                                     vehicle use -
                waters                  compaction and                                 disturbance of
                                        erosion                                        wildlife
                Oil leakage/spills -
                water pollution         Oil leakage/spills
                                        soil pollution
                Soil sealing -
                increased runoff,
                decreased
                infiltration to
                groundwater
Recreation      Increased use of        Trampling leading       Infrastructure         Increased
                water - reduction of    to erosion and          development            number of visitors
                water availability      compaction              (access roads,         in forests -wildlife
                and pollution                                   recreation centres     disturbance
                through effluent                                etc.) -changes in
                from tourist centres,                           landscape              Recreational
                camping grounds                                                        infrastructure
                etc.                                                                   development -
                                                                                       increased
                                                                                       groundwater
                                                                                       abstraction
                                                                                       affecting tree
                                                                                       growth
Grazing and         Overdensity of          Overdensity of          Overdensity of          Overgrazing and
browsing            grazing/browsing        grazing/browsing        grazing/browsing        browsing
                    animals - soil          animals  soil          animals - soil          (overpopulation
                    erosion and             erosion and             erosion and             of game) -
                    compaction -            compaction              changes in              damage to young
                    increased sediment                              landscape               plants, trees and
                    load, decreased                                                         habitats
                    infiltration to
                    groundwater

                Every day 100 species become extinct (four species per hour) due to tropical
                 deforestation.
                At the current rates, 5-10 per cent of tropical forest species will become
                 extinct every decade.
                Rainforests are being destroyed 40 per cent faster today than 10 years ago.
                At the current rates of deforestation, all tropical forests in the Philippines and
                 Madagascar will be destroyed within 20 years.
                Every year about 40 million hectares of rainforest are completely destroyed
                Almost 90 per cent of West Africa's rainforest has already been destroyed
                Asia lost almost a third of its tropical forest cover between 1960 and 1980 -
                 the highest rate of forest conversion in the world.

              The effects of deforestation

              Deforestation disrupts the closed system of nutrient cycling within tropical
              rainforests. Inorganic elements are released through burning and are quickly
              flushed out of the system by the high intensity rains.

              Soil erosion is also associated with deforestation. As a result of soil compaction,
              there is a decrease in infiltration, an increase in overland runoff and surface
              erosion.

              Sandification is a process of selective erosion. Raindrop impact washes away
              the finer particles of clay and humus, leaving behind the coarser and heavier
              sand.

              As a result of the intense surface runoff and soil erosion, rivers have a higher
              flood peak and a shorter time lag. However, in the dry season river levels are
              lower, the rivers have greater turbidity (murkiness due to more sediment), an
              increased bed load, and carry more silt and clay in suspension.

              Other changes relate to the climate. As deforestation progresses, there is a
              reduction in the water that is re-evaporated from the vegetation and so the
              recycling of water diminishes. Thus meaning annual rainfall is reduced, and the
              seasonality of rainfall increases. Evapotranspiration rates from savanna
              grasslands are estimated to be only about one-third of that of the tropical
              rainforest.

             Figure 16 Impacts of deforestation
   Hydrosphere                        Atmosphere                               Biosphere
   increased runoff                   increased turbidity                      increased sedimentation
   increased discharge leads to       O2 content reduced                       less CO2 absorbed
   flooding
   CO2 released from decaying         reduction in shading (more               increased evaporation
   woody material                     direct sunlight on forest floor)
   loss of biomass                    decrease in habitats                     decrease in species diversity
   rapid soil erosion leads to        increased leaching
   loss of nutrients

              Management
              From its establishment in 1991 until 1998, Ranomafana National Park was
operated by the Institute for the Conservation of Tropical Environments (ICTE)
at the State University of New York at Stony Brook. On 30 June 1998
management of the park was transferred to the national park service of
Madagascar, ANGAP (Association pour la Gestion des Aires Protégées).
ANGAP maintains a staff of approximately 80 to manage the park, including a
Park Manager, Chief Financial Officer, and Heads of Tourism, Conservation,
Ecological Monitoring, Conservation Education, and Community Relations.

Park organisation
The Ranomafana National Park and its surrounding communities are the focus
of an integrated conservation and development project (ICDP) funded in part by
the US government and private foundations. The Ranomafana National Park
Project (RNPP) was developed in response to Madagascar's 15-year National
Environmental Action Plan. The goals of the RNPP were to:
        establish Ranomafana National Park
        promote sustainable development for villagers affected by the park and
        conserve the biodiversity of the park.

The park is divided into a core protected zone of 41,500ha surrounded by a
peripheral zone in which some exploitation of the forest is permitted. The
peripheral zone contains more than 100 villages with over 25,000 residents in
total, most of whom are subsistence farmers.

The mission of the Ranomafana National Park is to:

 promote research on the biodiversity and conservation of Madagascar
  rainforests, including populations, communities, and the ecosystem processes
  they depend on
 promote formal and informal training at the undergraduate and graduate levels
  for international students and Malagasy scientists
 conduct long-term monitoring research on the flora and fauna of the park
 share information with Malagasy policy makers and with scientists globally.

However, not everyone was happy with the establishment of the park.
Complaints have been made that the parks were set aside without the consent
of the local people. When the Ranomafana Forest was converted into a national
park in 1991, 80,000 peasants who relied upon the forest as their primary
source of income viewed the transformation as an economic disaster. However,
had this park system not been implemented, it is estimated that there would
have been absolutely no forest cover left in 2025.

Other possible solutions to deforestation in Madagascar

One of the most important schemes for reducing the impact of deforestation is
debt-swapping. This is a scheme, initiated in the USA, whereby bankers in
MEDCs agree to wipe out the debts of the LEDC country by allowing the debts
to be purchased at a fraction of their face value and then used to finance
conservation work. For example, the World Bank controls the operations of the
Rio Tinto Zinc mining subsidiary - no investment is permitted without
reassurance on ecological restoration.

Another scheme is to change current methods of farming. Palm trees help
rainforest soils. They bring nutrients into the soil and thrive on the nutrient weak
soil of the rain forests. These palm trees help stabilise the soil and thus prevent
erosion while palm oil provides a useful source of income. Replanting of
vegetables, hardwoods, 'charcoal' thorns, particularly in a tree nursery close to
the Montagne D'Ambre National Park, is being funded by the Worldwide Fund
for Nature (WWF) in return for the farmers themselves acting as wardens.
‘Wildlife corridors' are being planted to link some of the remaining areas of
woodland.
In addition, changes in the methods of harvesting timber i.e. selective logging
rather than clear-cut logging allow forests to regenerate naturally. Ideally
logging in rainforests needs to be halted completely to ensure their safety but
this is unlikely.

Other potential solutions are smaller in scale. For example, the World Bank
directly finances some of the work of the WWF which co-ordinates many of the
individual projects being carried out on the island using its own funds and
support from the World Bank and from UNISAID (the United States Agency for
International Development), which in turn has been particularly heavily involved
in financing the Montagne Ambre conservation project. The Montaign d'Ambre
National Park is on a small rainforested mountain in the far north of
Madagascar, surrounded by dryer lowland.

Conclusion

Deforestation of Madagascar’s rainforest has been severe and rapid - most of
the losses have occurred within the last 70 years, and local people are the
major cause of the destruction.

Rapidly growing population pressure combined with extreme poverty threatens
these unique natural assets of Madagascar. There are many threats to the
forest around the park. Slash and burn agriculture by subsistence farmers,
timber exploitation, conversion to rangeland, and cutting of wood for fuel and
forest products are widespread. Rainforest biomes are difficult to conserve on
account of their fragility, specialisation and the lack of speed with which they
can adapt to change. There is an urgent need to study Madagascar's
biodiversity, not the least of which is to learn how best to conserve it for future
generations. Madagascar is seen as conservation 'flagship'. If an area of such
outstanding beauty and wildlife significance cannot be saved there may be little
hope for less spectacular parts of the world. Protected land covers a very small
part of the country and even within these areas very few of the parks and
reserves are actively policed.

Further references


http://www.panda.org/livingplanet
gives details of the Living Planet index, a measure of global biodiversity and its
change over time. This is updated annually.

http://www.ran.org_center/factsheets
provides access to the Rainforest Action Network which has some excellent
factsheets on tropical rainforests, rates of deforestation, users of rainforests,
climate change and the rainforest, species extinctions, corporations in the
rainforest and many more.

				
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