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Conservation and Sustainable Use of the Biosphere - WBGU

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

support for <strong>the</strong> tourism industry in <strong>the</strong> drawing up <strong>of</strong><br />

a uniform environmental quality seal in Germany<br />

will be <strong>the</strong> next focus <strong>of</strong> work.<br />

Indicators: improve comparability<br />

As yet <strong>the</strong>re are no globally uniform definitions on<br />

data collection <strong>and</strong> observation <strong>of</strong> developments in<br />

tourism. In order to be able to record <strong>and</strong> compare<br />

this all over <strong>the</strong> world, <strong>the</strong> relevant stipulations<br />

issued by <strong>the</strong> UN Statistics Commission in 1993<br />

should be adopted or harmonized with existing regulations.<br />

In this context, <strong>the</strong> external environmental<br />

costs induced by tourism should be entered on <strong>the</strong><br />

balance sheet as part <strong>of</strong> <strong>the</strong> national tourism statistics.The<br />

United Nations World Tourism Organization<br />

should be streng<strong>the</strong>ned in its role (continuation <strong>and</strong><br />

updating guidelines, statistical surveys <strong>and</strong> monitoring<br />

as well as global reporting). International nature<br />

conservation NGOs (IUCN, WWF, etc) should also<br />

be involved.<br />

E 3.7.5<br />

Investigating <strong>the</strong> limits <strong>of</strong> carrying capacity for<br />

tourism<br />

There is a great need for knowledge on regional carrying<br />

capacity limits for tourism, especially with<br />

respect to designating zones <strong>of</strong> specific intensity <strong>of</strong><br />

use. Studies should <strong>the</strong>refore be conducted into<br />

whe<strong>the</strong>r carrying capacity limits can be determined<br />

for individual natural l<strong>and</strong>scapes on <strong>the</strong> basis <strong>of</strong> ‘disturbance<br />

rates’ for animals <strong>and</strong> plants (Box E 3.7-1).<br />

E 3.8<br />

The role <strong>of</strong> sustainable urban development in<br />

biosphere conservation<br />

Settlements <strong>and</strong>, in particular, urban conglomerations<br />

are particularly intensively used by people.<br />

Under <strong>the</strong> aspect <strong>of</strong> sustainable l<strong>and</strong> use geared<br />

towards <strong>the</strong> protection <strong>of</strong> <strong>the</strong> biosphere <strong>the</strong>y should<br />

be assigned to <strong>the</strong> l<strong>and</strong>scape use type ‘<strong>Conservation</strong><br />

despite use’ (Section E 3.4). The link between towns<br />

<strong>and</strong> <strong>the</strong> biosphere can be seen in <strong>the</strong>ir reciprocal significance:<br />

<strong>the</strong> quality <strong>of</strong> <strong>the</strong> biosphere has an important<br />

function for towns, <strong>and</strong> at <strong>the</strong> same time towns<br />

also perform functions for <strong>the</strong> conservation <strong>of</strong> <strong>the</strong><br />

biosphere. Towns have <strong>the</strong> greatest influence on <strong>the</strong><br />

biosphere through <strong>the</strong>ir high consumption <strong>of</strong><br />

resources <strong>and</strong> emission <strong>of</strong> pollutants, which also<br />

makes <strong>the</strong>m an important starting point for biosphere<br />

policy.<br />

E 3.8.1<br />

The key role <strong>of</strong> towns <strong>and</strong> cities in sustainable<br />

development<br />

Towns play a key role with regard to global sustainable<br />

development. 60 per cent <strong>of</strong> global GNP is produced<br />

in towns, <strong>and</strong> corresponding quantities <strong>of</strong><br />

resources are consumed. In absolute figures, for<br />

example, a European city with 1 million inhabitants<br />

has an average daily consumption <strong>of</strong> 320,000 tonnes<br />

water, 11,500 tonnes fossil fuels <strong>and</strong> 2,000 tonnes<br />

food. By <strong>the</strong> same token, every day 1,600 tonnes<br />

waste, 300,000 tonnes sewage <strong>and</strong> 1,500 tonnes air<br />

pollution are produced (Forum Umwelt und<br />

Entwicklung, 1996). The import <strong>and</strong> export <strong>of</strong><br />

resources <strong>and</strong> waste products brings additional pollution,<br />

meaning that <strong>the</strong>re is an externalization <strong>of</strong><br />

urban environmental problems which harm <strong>the</strong> biosphere.<br />

In addition, towns are becoming ever more important<br />

with regard to <strong>the</strong> social dimension <strong>of</strong> sustainable<br />

development. Whereas 45 per cent <strong>of</strong> people in<br />

<strong>the</strong> world lived in towns in 1995, in 2025 this figure<br />

will probably be 61 per cent (WRI, 1996). At <strong>the</strong><br />

same time, urban unemployment, homelessness,<br />

crime, social disparities <strong>and</strong> environmental pollution<br />

will increase. Hence concepts for sustainable development<br />

will have to prove <strong>the</strong>mselves equal to <strong>the</strong>se<br />

issues. Approaches for a biosphere policy will <strong>the</strong>refore<br />

have to aim at sustainable urban development.<br />

This not only comprises <strong>the</strong> conservation <strong>and</strong> sustainable<br />

use <strong>of</strong> <strong>the</strong> biosphere within towns, but also a<br />

long-term change <strong>of</strong> urban processes <strong>and</strong> lifestyles.<br />

To do this it is first <strong>of</strong> all necessary to describe <strong>the</strong><br />

special features <strong>of</strong> <strong>the</strong> urban ecosystem, especially<br />

with regard to <strong>the</strong> differences from non-urban or biological<br />

ecosystems (Table E 1.2-1).<br />

E 3.8.2<br />

Special features <strong>of</strong> urban ecosystems<br />

There are causal <strong>and</strong> functional interactions between<br />

<strong>the</strong> system elements <strong>of</strong> an ecosystem (Section E 1.1),<br />

which determine <strong>the</strong> processes within an ecosystem<br />

<strong>and</strong>, at <strong>the</strong> same time, demarcate it from o<strong>the</strong>r<br />

ecosystems (‘functional ecosystem’). However,<br />

ecosystems can also be demarcated from one ano<strong>the</strong>r<br />

on <strong>the</strong> basis <strong>of</strong> a naturally bounded, coherent space,<br />

eg a lake or a forest (‘geographic ecosystem’). Due to<br />

its significant fragmentation, a town is not a functional<br />

ecosystem, but as an ecosystem complex <strong>and</strong> a<br />

demarcated space it corresponds to a geographic<br />

ecosystem (Trepl, 1994). Even if cities cannot be considered<br />

as independent functional ecosystems, <strong>the</strong>y

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