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Conservation and Sustainable Use of the Biosphere - WBGU

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16 C The biosphere-centred network <strong>of</strong> interrelations<br />

Continent Area Undisturbed Partially Dominated<br />

disturbed by man<br />

[km 2 ] [%]<br />

Europe 5,759,321 15.6 19.6 64.9<br />

Asia 53,311,557 42.2 29.1 28.7<br />

Africa 33,985,316 48.9 35.8 15.4<br />

North America 26,179,907 56.3 18.8 24.9<br />

South America 20,120,346 62.5 22.5 15.1<br />

Australasia 9,487,262 62.3 25.8 12.0<br />

Antarctica 13,208,983 100.0 0.0 0.0<br />

World as a whole 162,052,691 51.9 24.2 23.9<br />

World as a whole 134,904,471 27.0 36.7 36.3<br />

(without rocky <strong>and</strong> ice<br />

regions <strong>and</strong> infertile l<strong>and</strong>)<br />

Table C 1.1-1<br />

Human influence on<br />

ecosystems worldwide. The<br />

following criteria were<br />

considered: vegetation<br />

(primary, secondary, type <strong>of</strong><br />

agriculture <strong>and</strong> forestry),<br />

population density, human<br />

settlement <strong>and</strong> l<strong>and</strong><br />

degradation (eg<br />

desertification).<br />

Source: after Hannah et al,<br />

1994<br />

pasturel<strong>and</strong> or plantations, <strong>and</strong> natural watercourses<br />

into canals. This form <strong>of</strong> change in l<strong>and</strong> use is a key<br />

factor in global change <strong>and</strong> possibly <strong>the</strong> most important<br />

reason for <strong>the</strong> loss <strong>of</strong> biological diversity (UNEP,<br />

1995). For example, <strong>the</strong> loss <strong>of</strong> l<strong>and</strong> through conversion<br />

is cited at 68 per cent for <strong>the</strong> Indo-Malay countries<br />

<strong>and</strong> 65 per cent for <strong>the</strong> tropical countries in<br />

Africa (MacKinnon <strong>and</strong> MacKinnon, 1986). Today,<br />

only 27 per cent <strong>of</strong> <strong>the</strong> Earth’s surface covered by<br />

vegetation is classed as undisturbed by humans<br />

(Table C 1.1-1).<br />

This trend can be differentiated from <strong>the</strong> trend <strong>of</strong><br />

degradation <strong>of</strong> natural ecosystems, in which <strong>the</strong>re is<br />

no direct destruction <strong>of</strong> natural structures but a<br />

mostly slow, anthropogenic influence that is marked<br />

by a gradual loss <strong>of</strong> structures or functions (UNEP,<br />

1995). In order to allow an exact differentiation <strong>the</strong><br />

trend degradation <strong>of</strong> natural ecosystems has been<br />

sub-divided into <strong>the</strong> three trends below.<br />

Fragmentation <strong>of</strong> natural ecosystems<br />

Fragmentation means <strong>the</strong> spatial breakdown <strong>of</strong> formerly<br />

coherent natural ecosystems into smaller, isolated<br />

partial areas, which, for example, arise through<br />

<strong>the</strong> construction <strong>of</strong> transport infrastructure or<br />

through conversion (Noss <strong>and</strong> Csuti, 1997). As a<br />

result <strong>of</strong> this, <strong>the</strong> habitats <strong>of</strong> individual species are<br />

made smaller <strong>and</strong> <strong>the</strong> populations are isolated from<br />

each o<strong>the</strong>r. Fragmentation slows down <strong>the</strong> genetic<br />

exchange between populations or can even bring it to<br />

a st<strong>and</strong>still, with <strong>the</strong> result that <strong>the</strong>re is a gradual loss<br />

<strong>of</strong> species in <strong>the</strong> fragments. Fragmentation can frequently<br />

be seen after a large-scale conversion, eg <strong>the</strong><br />

areas excluded from <strong>the</strong> clearance <strong>of</strong> primary forest<br />

form individual ‘isl<strong>and</strong>s’ in <strong>the</strong> midst <strong>of</strong> arable l<strong>and</strong>,<br />

pasturel<strong>and</strong> or secondary vegetation that are <strong>of</strong>ten<br />

too small to ensure <strong>the</strong> long-term functioning <strong>of</strong> <strong>the</strong><br />

partial ecosystems. Both globally <strong>and</strong> regionally, fragmentation<br />

is one <strong>of</strong> <strong>the</strong> major threats to biological<br />

diversity (WRI et al, 1992).<br />

Damage to ecosystem structure <strong>and</strong><br />

functions<br />

This addresses <strong>the</strong> loss <strong>of</strong> functional units in an<br />

ecosystem, which, for example, can be triggered by<br />

<strong>the</strong> extinction <strong>of</strong> dominant species or keystone<br />

species (Section D 2), by immigration <strong>of</strong> alien species<br />

(Section E 3.6) or by substance overload (Section<br />

E 3.2). As a result, <strong>the</strong> functional interactions<br />

between <strong>the</strong> species (eg food webs) are modified in<br />

such a way that <strong>the</strong> ecosystem changes greatly (triggering<br />

succession) or <strong>the</strong> original ecological services<br />

can only be performed to a limited extent (UNEP,<br />

1995).<br />

Substance overload <strong>of</strong> natural ecosystems<br />

There are a large number <strong>of</strong> substances that exert<br />

negative influences on ecosystems. Excessive loading<br />

with organic (degradable) substances <strong>and</strong> nutrient<br />

salts (eg nitrate, phosphate) can trigger eutrophication<br />

in lakes, rivers <strong>and</strong> streams <strong>and</strong> coastal waters<br />

<strong>and</strong> put <strong>the</strong> groundwater at risk. Inputs <strong>of</strong> pollutants<br />

from <strong>the</strong> air (eg SO 2<br />

,NO x<br />

) <strong>and</strong> <strong>the</strong> resultant acid rain<br />

damage forests <strong>and</strong> lakes. Organochlorine pesticides<br />

(eg DDT or lindane) from agriculture <strong>and</strong> forestry<br />

that biodegrade slowly (persistent) can cause direct<br />

damage, but also have an indirect effect via accumulation<br />

in food chains. Not least, a wide variety <strong>of</strong> toxic<br />

substances reach <strong>the</strong> biosphere from many sources:<br />

eg mercury pollutes South American rivers <strong>and</strong><br />

streams as a result <strong>of</strong> gold mining, cyanides are used<br />

for fisheries in sou<strong>the</strong>ast Asian reefs (Section E 2.4),<br />

dioxin is released into <strong>the</strong> environment from industrial<br />

processes or radioactive waste is disposed <strong>of</strong> at<br />

sea (radiation). The consequence <strong>of</strong> this substance<br />

deposition is that today no spot on Earth can be considered<br />

to be free <strong>of</strong> anthropogenic pollution.<br />

Genetic <strong>and</strong> species loss<br />

Genetic <strong>and</strong> species loss is a major consequence <strong>of</strong><br />

<strong>the</strong> above-mentioned ecosystem trends (<strong>WBGU</strong>,

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