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Conservation and Sustainable Use of the Biosphere - WBGU

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304 I Global biosphere policy<br />

high degree <strong>of</strong> diversity, a range <strong>of</strong> extreme abiotic<br />

<strong>and</strong> biotic conditions <strong>and</strong> an unbroken tradition in<br />

<strong>the</strong> indigenous population, <strong>the</strong> option value <strong>of</strong> <strong>the</strong>se<br />

natural resources is particularly high. In order to preserve<br />

<strong>the</strong> option value <strong>of</strong> hi<strong>the</strong>rto unknown species<br />

<strong>and</strong> forms <strong>of</strong> use for future generations, areas <strong>of</strong> natural<br />

or semi-natural ecosystems must be conserved<br />

<strong>and</strong> certain human uses such as commercial extraction<br />

<strong>of</strong> biomass, hunting <strong>and</strong> fishing precluded. The<br />

regions must be differentiated in terms <strong>of</strong> <strong>the</strong> numbers<br />

<strong>of</strong> endangered species. It is too risky to provide<br />

just one protected area per species or ecosystem, so<br />

several representative areas need to be protected in<br />

order to ensure <strong>the</strong> long-term protection goal. And<br />

<strong>the</strong> protected areas need to be cross-linked into <strong>the</strong><br />

l<strong>and</strong>scape (Section E 3.3.2). As far as we know some<br />

ecosystems <strong>and</strong> species react extremely sensitively to<br />

human influence, which means that a certain portion<br />

<strong>of</strong> <strong>the</strong> biosphere needs total protection against human<br />

influences. Enforcing this sort <strong>of</strong> protection that is<br />

based on values that cannot be translated directly<br />

into monetary terms <strong>and</strong> that cannot be developed<br />

until some point in <strong>the</strong> future in <strong>the</strong> face <strong>of</strong> concrete,<br />

conflicting interests is a particular challenge.<br />

The Council is aware that a scientifically grounded<br />

‘water-tight’ derivation <strong>of</strong> a guard rail in <strong>the</strong> form <strong>of</strong><br />

protected area targets is not possible at <strong>the</strong> present<br />

time. If, however, here <strong>the</strong> figure <strong>of</strong> 10–20 per cent <strong>of</strong><br />

terrestrial area is given, <strong>the</strong>n this is a broad estimate<br />

that is mainly founded on expert intuition (Section E<br />

3.3.2). This figure will however vary greatly from<br />

region to region, depending on <strong>the</strong> natural status <strong>and</strong><br />

features. Since such areas are generally also interesting<br />

for o<strong>the</strong>r reasons (eg protection <strong>of</strong> <strong>the</strong> existence<br />

value) <strong>the</strong>re are synergies with <strong>the</strong> guard rail for <strong>the</strong><br />

preservation <strong>of</strong> <strong>the</strong> global natural heritage (Section I<br />

1.4).And this percentage already includes <strong>the</strong> preservation<br />

<strong>of</strong> populations <strong>and</strong> species for reasons <strong>of</strong> existence<br />

value (Section I 1.4) <strong>and</strong> option value.<br />

I 1.4<br />

Fourth biological imperative: preserve <strong>the</strong> global<br />

natural heritage<br />

The preamble to <strong>the</strong> Convention on Biological<br />

Diversity affirms that biological diversity is a ‘common<br />

concern <strong>of</strong> humankind’. Similar formulations in<br />

o<strong>the</strong>r agreements on <strong>the</strong> biosphere, AGENDA 21 <strong>and</strong><br />

<strong>the</strong> programmes <strong>of</strong> international institutions permit<br />

<strong>the</strong> conclusion that in <strong>the</strong> international community a<br />

global consensus in favour <strong>of</strong> preserving <strong>the</strong> natural<br />

heritage <strong>of</strong> creation has been established. According<br />

to this consensus it is unacceptable to allow large<br />

losses <strong>of</strong> worldwide biological diversity. The reasons<br />

for this are varied <strong>and</strong> <strong>the</strong>y have been explained at<br />

various points in this report: <strong>the</strong>y range from concrete<br />

‘survival arguments’ (without <strong>the</strong> maintenance<br />

<strong>of</strong> agrobiodiversity <strong>the</strong> world’s food is in danger, Sections<br />

D 3.4 <strong>and</strong> I 1.2) to more normative rationales<br />

(existential <strong>and</strong> symbolic value; preservation <strong>of</strong> a natural<br />

heritage site can be rationalized in a similar way<br />

as monuments are preserved as world cultural heritage<br />

sites; Chapter H). And, ultimately, this guard<br />

rail also has consequences in <strong>the</strong> form <strong>of</strong> claims to<br />

territory, ie nature conservation becoming in certain<br />

areas <strong>the</strong> primary form <strong>of</strong> ‘l<strong>and</strong> use’ (Section E 3.3.2).<br />

L<strong>and</strong>scapes <strong>and</strong> ecosystems<br />

Here, first <strong>of</strong> all we should name <strong>the</strong> parts <strong>of</strong> <strong>the</strong> biosphere<br />

that according to <strong>the</strong> UNESCO convention<br />

<strong>and</strong> o<strong>the</strong>r territory-specific conventions make up <strong>the</strong><br />

natural heritage <strong>of</strong> humankind <strong>and</strong> <strong>the</strong>refore enjoy<br />

special protection (Section I 3). Just as <strong>the</strong> loss <strong>of</strong> cultural<br />

treasures that have been acquired over <strong>the</strong><br />

course <strong>of</strong> <strong>the</strong> cultural evolution <strong>of</strong> humankind is<br />

unacceptable for <strong>the</strong> global community, a global consensus<br />

has been established on <strong>the</strong> basis <strong>of</strong> <strong>the</strong> high<br />

existential <strong>and</strong> symbolic value also to preserve <strong>the</strong><br />

natural treasures <strong>of</strong> biological evolution or geologically<br />

valuable formations. These include places such<br />

as Lake Baikal, Yellowstone National Park or <strong>the</strong><br />

Serengeti.These ‘jewels <strong>of</strong> <strong>the</strong> biosphere’ are in many<br />

instances already under national <strong>and</strong> international<br />

protection (eg through <strong>the</strong> World Heritage Convention,<br />

Section I 3.3.1) but in many cases require additional<br />

support, particularly if <strong>the</strong> capacity <strong>of</strong> <strong>the</strong><br />

respective country – <strong>of</strong>ten a developing country – is<br />

strained.<br />

These ‘jewels’ that are already protected should in<br />

a global approach be supplemented by representative<br />

sections <strong>of</strong> all <strong>of</strong> <strong>the</strong> major ecosystems <strong>of</strong> <strong>the</strong><br />

Earth. The dem<strong>and</strong> that no ecosystem type may be<br />

allowed to disappear is much easier to implement<br />

than is that same dem<strong>and</strong> applied to species, even<br />

though <strong>the</strong>re have already been irrevocable losses in<br />

<strong>the</strong> area <strong>of</strong> ecosystems. To this end it will require a<br />

network <strong>of</strong> protected areas that includes representative<br />

examples <strong>of</strong> all natural ecosystem types (Section<br />

E 3.3.2). Topological aspects must be taken into particular<br />

consideration when selecting areas (habitat<br />

connectivity, corridors, stepping stone ecosystems).<br />

From <strong>the</strong>se thoughts recommendations for l<strong>and</strong>scapes<br />

<strong>and</strong> ecosystems can be derived:<br />

• They must incorporate areas already under protection.<br />

• Following a gap analysis in <strong>the</strong> current representative<br />

nature <strong>of</strong> <strong>the</strong> protected area system <strong>the</strong>y<br />

would have to include <strong>the</strong> missing areas. This<br />

analysis is time-consuming <strong>and</strong> cannot be carried<br />

out by <strong>the</strong> Council at this point. This approach<br />

could be calculated on <strong>the</strong> basis <strong>of</strong> <strong>the</strong> various

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