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Convention on biological diversity


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MECHANISMS


Deficiencies in the flow of information to decision-makers and to local communities

Unsustainable consumption and production patterns

Human population growth and density





Deficiencies in scientific knowledge & in the use of local knowledge


Fig. 1: Main causes of forest biological diversity loss (CIFOR, 2000)

Agricultural development



Globalization and the rise of corporate power

Under-valuation FBD goods and services

Perverse incentives and subsidies and ill-defined develop ment programmes

Uncontrolled forest fires, slash and burn

Ill-defined or uninforced regulatory mechanisms

Lack of capacity and limited resources to undertake conservation or management actions

Lack of EIAs and SEAs

Political unrest, war

Inappropriate application of Structural Adjustment

Invasive species

Historical, social, political and economic context of the country


    B
    Unsustainable levels of consumption and production

    Human population growth and density

    . An historical and present perspective of forest biological diversity



Current concerns over the rates of loss of biological diversity as a consequence of human population growth and resource use have been well-documented (Pimm et al., 1995, UNEP 1995, WRI 2000). However, loss of species, including forest dependent species, is an evolutionary fact, as evidenced through the fossil record, which suggests that 95 per cent of the species that have ever lived are now extinct (Raup, 1991). Several major periods of mass extinction are clearly shown in the fossil record, with the last mass extinction being about 65 millions years ago, at the end of the Cretaceous period. Aside from catastrophic mass extinction, a continuous background extinction rate has also been variously estimated, depending on taxon and species concerned. Interestingly, the background extinction rate appears to have declined for most taxa (Valentine et al., 1991) except terrestrial flora, where the rate has increased (Niklas et al., 1985). Numerous theories have been advanced to explain both background and mass extinctions and debate continues. However, species accumulation seems to occur in geologic time following each extinction event (Jablonbski, 1991).

While the causes of past extinctions remain under debate, the recent phenomenal rate of extinctions associated with humans has been substantiated for a few cases, some noted in Pimm et al. (1995). Humans have caused extinctions for several thousands of years (Martin, 1973). A particular example is the Polynesian occupation of Pacific islands, which resulted in the extinction of more than 2000 bird species [reference needed]. In the north-eastern United States and southern Canada, an area with trees was logged continuously since European colonisation. During that period, four of 26 endemic bird species (16%) have gone extinct and it has been calculated that humans now cause about 1000 - 10000 extinctions per million species-years (Pimm et al., 1995). Extinction is not always a rapid process. Many species may be driven to extinction over several hundred years by now immutable processes. However, in the 15th and 16th centuries, the global spread of European cultures and their livestock, crops, weeds and diseases increased the loss of island flora and fauna and added to the threats to continental species. In later centuries, the growth of trans-oceanic human travel and commerce led to the spread of a tremendous variety of species to new regions of the world and human colonisation of many uninhabited islands. Native species may be out-competed by the exotic species introduced, deliberately or accidentally, by humans. Current estimated rates of extinction for most higher life-forms in tropical rain forests are 1-10% of these species in the next 25 years (or 1000 to 10,000 times background rates) (UNEP, 1995).

Causes of extinction are many: Allee effects in small populations, environmental change, demographic and genetic stochasticity, excessive killing by humans, competition from exotic species, habitat loss and fragmentation and other habitat changes (Box 5). Most extinctions faced by contemporary animal species are the result of habitat loss and competition (or predation) by exotic species (WCMC, 1992). Indeed, habitat loss is the major threat to 75% of endangered birds (Pimm et al., 1995). For trees, the number of species at risk is largely a result of logging and clearing for agriculture, which together threaten about 2300 species (Oldfield et al., 1998).

Extinctions may be caused by isolation of populations, followed by inbreeding and loss of fitness to react to environmental changes, competition and natural selection (see Chapter 1). Lessons from population genetics indicate that in forest areas, large areas of habitat must exist to maintain populations of large-bodied species, there must be connections between habitat patches to enable gene flow, populations should always be larger than that which is minimally viable, there should be multiple separate populations to avoid loss by local catastrophic events, and great care should be taken with island ecosystems. Of course, in biological systems, cascading effects can result from individual extinctions, when a species with particular functional importance to an ecosystem (keystone species) is removed (see earlier chapters).

Some countries are attempting to redevelop historical forest types, based on retrospective studies of biodiversity and forest structures. The idea is to establish a ‘benchmark’ of forest types, structures and age classes in the landscape and then to try and redevelop historical ecosystems through silvicultural techniques. For instance, in eastern Canada, which has had a history of clearcutting and high-grade logging over 300 years, several important conifer species, such as white pine (Pinus strobus), red spruce (Picea rubens) and eastern hemlock (Tsuga canadensis) have been severely depleted. Redevelopment of the historical forest ecosystem, as part of the biodiversity objectives set for the forest, is occurring within the Canadian Model Forest Network Programme (see Box 9 in Chapter IV).


    C. Direct causes of loss of forest biodiversity

The direct cause of forest biodiversity loss is forest decline, in particular the destruction and/or degradation of natural and semi-natural forest ecosystems (WRI et al., 1992; WCMC, 1992; Barbier et al., 1994a; ESD, 1995; Stedman-Edwards, 1998). In general, all forest types are affected by deforestation and degradation. However, at a global level the forest associations which have already disappeared or are at most risk in the future are those occupying habitats most suited to agricultural development, notably lowland forests and woodland communities on flatter terrain with fertile soils. In addition, various riparian forest ecosystems have greatly diminished in extent and quality due to agricultural development, reduced water flows and/or inundation for dam development (irrigation and hydro-power) and severe flooding events due to catchment changes and/or climate change. Forests associated with certain mineral ore bodies have also suffered or remain at high risk, e.g. specialised floras on nickel- and heavy metal-rich ultramafic soils in New Caledonia and the Solomon Islands in the south-west Pacific.

As mentioned earlier, human actions are the most important direct cause of forest loss. Their destructive actions include: adverse agriculture practices (conversion to agricultural land and industrial agriculture, overgrazing and unmitigated shifting cultivation); unsustainable forest management (such as poor logging practices, over-exploitation of wood for fuel and charcoal manufacture, over collection of non-timber forest resources); introduction of exotic and/or invasive plant and animal species; infrastructure development (road building, hydro-electrical development, improperly planned recreational activities); mining and oil exploitation. In addition, human cause forest fires, pollution and climate change all of which are likely to lead to forest loss.



At the species level, extinction is commonly associated with extreme rarity, and insufficient reproductive capacity: the six main direct causes of species extinction being habitat loss and degradation, fragmentation, overexploitation, secondary extinction, introduction of exotic species and climate change (Diamond, 1984; Terborgh and van Schaik, 1997). Loss of genetic diversity in a species can be associated with loss of genetically distinctive populations, especially in those species with high levels of between-population variation. The main causes of local extinction or the loss of a particular population are the same as those for loss of a species.

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