Conservation and Sustainable Use of the Biosphere - WBGU
Conservation and Sustainable Use of the Biosphere - WBGU
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.