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Berlin Environmental Atlas

01.02 Impervious Soil Coverage (Sealing of Soil Surface) (Edition 2012)

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Excursus

Comparison of the impervious coverage data for 2011 and 2005 with the Impervious Coverage Indicator of the Working Group on Integrated Environmental and Economic Accounting of the German States (EEAL; Ger.: UGRdL)

The impervious coverage value for Berlin of the Working Group on Integrated Environmental and Economic Accounting of the German States (EEAL), developed by the Federal-State Commission on Soil Protection (LABO) on the bases of the sustainability indicator "land consumption for residential/ commercial and traffic areas", is now juxtaposed to the results of the Environmental Atlas.

The data survey of degrees of impervious coverage by state is based on official land statistics, in which estimated degrees of impervious coverage are assigned to various use categories of residential/ commercial and traffic areas, modified in accordance with residential density of the areas, and then used as a factor in calculation. In this way, impervious coverage data can be generated on an annual basis. The data on development of impervious coverage in the states are updated annually (EEAL 2010).
Accordingly, the proportion of impervious coverage in the total area of Berlin rose from 34.24 % in 2000 to 35.10 % in 2010, and thus increased by 0.86 % in 10 years, which comes to an annual rate of increase of 0.09 %. The absolute increase in impervious coverage was thus 770 ha during that ten-year period.

Figure 9 shows the rate of impervious coverage of the Environmental Atlas in 2005 and 2011, compared with the annually generated data of the EEAL.

Neither approach ascertains impervious coverage precisely; both work with different methods and different goals, and, to a certain extent, with estimates and assumptions, and are thus ultimately estimation methods.

While the EEAL approach gives the current (2010) overall impervious coverage of Berlin as 35.1 %, the Environmental Atlas mapped only 32.8 % of the city as impervious in 2011.

Under the procedure of the Environmental Atlas, the built-up impervious coverage area was derived directly from the ALK, and hence has a very high degree of precision, while the non-built-up impervious coverage area, as described above, is determined from satellite imagery. Hence, the above-mentioned error sources must be methodologically taken into account.

By contrast, the EEAL approach operates from the outset with estimates for certain use classes, which are moreover nationally uniform, and hence do not take regional particularities into account. For instance, the elimination of the area of Tempelhof Airport for the category of traffic areas at the time of its closure led to a change in the statistical situation, in spite of the fact that nothing changed in real life.

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Fig. 9: Degrees of impervious coverage shown in the Environmental Atlas, 2005 in 2011 Editions, compared with the annually generated data of the EEAL

Excel
[Statistical base of the Figure is also available as Excel-File (MS-Excel is required).]

For political decision-making, other impervious coverage data can also be used. The impervious coverage data of the EEAL is collected annually according to a fixed, nationally uniform comparison method, and is thus best suited for monitoring, and ultimately, too, has been developed precisely for that purpose. Due to the ability to differentiate between built-up impervious areas, non-built-up impervious areas, and impervious street surfaces, the Environmental Atlas figures complement and modify the figures of the EEAL data. For built-up impervious surfaces, a very high degree of precision can be assumed.

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