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Conservation and Sustainable Use of the Biosphere - WBGU

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150 E Diversity <strong>of</strong> l<strong>and</strong>scapes <strong>and</strong> ecosystems<br />

Box E 3.3-6<br />

Forests <strong>and</strong> biological diversity<br />

The loss <strong>of</strong> forest biodiversity results both from <strong>the</strong> loss <strong>of</strong><br />

forest l<strong>and</strong> (Section E 3.3.4.4) <strong>and</strong> from <strong>the</strong> degradation <strong>of</strong><br />

existing forests. Both processes continue apace <strong>and</strong>, after<br />

centuries <strong>of</strong> forest destruction in temperate <strong>and</strong> boreal<br />

areas, since <strong>the</strong> mid-twentieth century <strong>the</strong>y have taken<br />

place particularly actively in <strong>the</strong> tropics. With regard to <strong>the</strong><br />

loss <strong>of</strong> biological diversity, special importance is attached to<br />

<strong>the</strong> loss <strong>of</strong> tropical forests <strong>and</strong> forest degradation because<br />

<strong>the</strong> tropical forests are disproportionately richer in species<br />

than temperate <strong>and</strong> boreal forests <strong>and</strong> <strong>the</strong> agro-ecosystems<br />

that result from <strong>the</strong> conversion are much more fragile.<br />

The best contribution to <strong>the</strong> conservation <strong>of</strong> forest biological<br />

diversity can be made by <strong>the</strong> biodiversity <strong>of</strong> forests<br />

being understood as a carrier <strong>of</strong> biological resources. The<br />

value <strong>of</strong> <strong>the</strong>se biological resources comes to bear at various<br />

levels, ranging from <strong>the</strong> household level (firewood, food,<br />

medicine), local (food, firewood, medicine, building materials),<br />

national (wood products, water, firewood, etc) <strong>and</strong><br />

international markets (wood products, resins, oils, tourism,<br />

etc) (Section H 5). Forest biodiversity gains global significance<br />

as an important carrier <strong>of</strong> information for future<br />

options on technological or medical developments (Section<br />

D 3.3). Fur<strong>the</strong>r importance may be attached to <strong>the</strong> biodiversity<br />

<strong>of</strong> forests regarding <strong>the</strong>ir stabilising effect on <strong>the</strong><br />

global climate (Section F 2). The importance <strong>of</strong> forests as<br />

biological carbon sinks is currently <strong>the</strong> subject <strong>of</strong> international<br />

discussion (<strong>WBGU</strong>, 1998b).<br />

The information on <strong>the</strong> number <strong>of</strong> species in forests is<br />

highly unreliable <strong>and</strong> fluctuates between 2 <strong>and</strong> 80 million<br />

species. The mean value <strong>of</strong> <strong>the</strong> estimates is around 10 million<br />

species, <strong>and</strong> it is assumed that <strong>the</strong> vast majority <strong>of</strong> <strong>the</strong>se<br />

are arthropods (WCMC, 1992; Heywood <strong>and</strong> Watson, 1995).<br />

In turn, around 50–90 per cent <strong>of</strong> arthropods are to be found<br />

in <strong>the</strong> tropical forests <strong>and</strong> this emphasizes <strong>the</strong>ir high fauna<br />

diversity. With respect to plant biodiversity <strong>the</strong> much<br />

quoted example form Borneo can be used, where 700 tree<br />

species have been identified on 10 ha <strong>of</strong> forestl<strong>and</strong>, in o<strong>the</strong>r<br />

words more species than occur in <strong>the</strong> whole <strong>of</strong> North America<br />

(Rodgers, 1996).<br />

In light <strong>of</strong> <strong>the</strong> pressure on l<strong>and</strong> use described above, fur<strong>the</strong>r<br />

losses <strong>of</strong> forests in <strong>the</strong> tropics will be inevitable (Chapter<br />

G). The majority <strong>of</strong> <strong>the</strong> conversion will continue to be<br />

for agricultural use. It is <strong>the</strong>refore all <strong>the</strong> more important to<br />

integrate <strong>the</strong> l<strong>and</strong> use changes into comprehensive concepts<br />

that are anchored at regional level (Section E 3.9). The<br />

maintenance <strong>of</strong> <strong>the</strong> agricultural productivity <strong>of</strong> <strong>the</strong> converted<br />

forestl<strong>and</strong> or increasing <strong>the</strong> productivity on existing<br />

agricultural l<strong>and</strong> must be an important objective (Section<br />

E 3.3.4.2).<br />

Although most national policies emphasize that <strong>the</strong><br />

remaining forestl<strong>and</strong> should be protected, deforestation<br />

continues on a global level. From this, it can be seen that <strong>the</strong><br />

causes <strong>of</strong> forest destruction are multi-faceted <strong>and</strong> differ<br />

from region to region. Not only direct reasons, such as <strong>the</strong><br />

spread <strong>of</strong> slash <strong>and</strong> burn, but also indirect reasons due to <strong>the</strong><br />

failure <strong>of</strong> policies, such as rural poverty, lead to <strong>the</strong> continuing<br />

destruction <strong>of</strong> forests (NNA, 1998; Jepma 1995; Pearce<br />

<strong>and</strong> Moran, 1998; Chapter G).<br />

Since <strong>the</strong> existing biological diversity <strong>of</strong> <strong>the</strong> forests cannot<br />

be preserved as a whole <strong>and</strong> species are becoming<br />

extinct more quickly than all <strong>the</strong> existing species can be<br />

recorded (Pimm et al, 1995; Section D 1), special significance<br />

is attached to <strong>the</strong> functional evaluation <strong>of</strong> biodiversity<br />

alongside recording habitats. Two questions can be<br />

asked:<br />

• How much biodiversity is needed to conserve multifunctional<br />

forests (Section E 3.3.9)?<br />

• Can this question be answered on time?<br />

The first steps along this route have been made with <strong>the</strong><br />

identification <strong>of</strong> hotspots <strong>of</strong> biodiversity, <strong>the</strong> designation <strong>of</strong><br />

indicator taxa <strong>and</strong> <strong>the</strong> mapping <strong>of</strong> <strong>the</strong> usage pressure on<br />

existing forest ecosystems (Global Forest Watch; WRI,<br />

1999).An accompanying measure that could help to reduce<br />

<strong>the</strong> predatory exploitation <strong>of</strong> forest resources is <strong>the</strong> certification<br />

<strong>of</strong> wood products <strong>and</strong> forms <strong>of</strong> management (Box<br />

E 3.3). A legally binding regulation for forest protection is<br />

long overdue (Section I 3.4.4). The instruments <strong>and</strong> means<br />

<strong>of</strong> implementation currently available are, however, so limited<br />

that it is extremely doubtful whe<strong>the</strong>r <strong>the</strong> dynamics <strong>of</strong><br />

<strong>the</strong> current trend can be decisively influenced.<br />

be minimized, far-reaching changes in eating habits<br />

<strong>and</strong> in <strong>the</strong> way we keep <strong>and</strong> use animals will have to<br />

be effected.<br />

• Overnutrition with foods <strong>of</strong> animal origin must be<br />

reduced because it is inefficient on <strong>the</strong> one h<strong>and</strong><br />

<strong>and</strong> has a negative impact on health on <strong>the</strong> o<strong>the</strong>r.<br />

• The productivity <strong>of</strong> domesticated animals should<br />

be optimized because large unproductive stocks<br />

have a disproportionate negative impact on biodiversity.<br />

This should also include ‘improvement’ <strong>of</strong><br />

traditional livestock breeds.<br />

• Grazing practices should be more oriented<br />

towards <strong>the</strong> carrying capacity <strong>of</strong> <strong>the</strong> grassl<strong>and</strong>s in<br />

order to prevent <strong>the</strong> degradation <strong>of</strong> <strong>the</strong> grazing<br />

areas.<br />

Switching to animal foodstuffs from <strong>the</strong> sea is also<br />

limited because some natural fish populations are<br />

already being overexploited. Although aquaculture<br />

is a possible alternative, high-quality feed must be<br />

used, which – in turn – mostly comes from terrestrial<br />

ecosystems. Also, establishing cultures <strong>of</strong> this kind in<br />

lakes <strong>and</strong> shallow seas is problematic from <strong>the</strong> point<br />

<strong>of</strong> view <strong>of</strong> environmental pollution <strong>and</strong> <strong>the</strong> impact on<br />

<strong>the</strong> biodiversity <strong>of</strong> aquatic ecosystems (Section<br />

E 3.4).<br />

The production <strong>of</strong> food using biotechnological<br />

methods has not yet progressed to a level where it<br />

can relieve shortages. Although <strong>the</strong>re is great potential<br />

for <strong>the</strong> biological conversion <strong>of</strong> plant wastes or<br />

residues into feedstuffs <strong>and</strong> foods, only a few<br />

approaches have so far proved to be economically<br />

sustainable. New information <strong>and</strong> conversion methods<br />

should be developed for <strong>the</strong> better use <strong>of</strong> plant<br />

biomass (such as wood or straw) as feed <strong>and</strong> food. In<br />

this respect, molecular biological methods could<br />

open up new opportunities.

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