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Preface
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1.Climate as a Public Interest in Planning and Zoning
2.Characteristics and Forms of the Urban Climate
2.1Overview
2.2Urban Heat Budget
2.3Urban Heat Islands
2.4Humidity / Precipitation / Vegetation
2.5Wind
2.6Bioclimate
2.7Air Exchange
2.8Pollutant Emissions
2.8.1The Traffic as Pollutant Source
2.8.2Computational Estimation of Traffic Immissions
2.9Pollutant Levels and Threshold Values
2.9.1Limits and Assessment values
2.10Effect of Pollutant
2.11Climate Change
2.11.1Climate Change in Germany
2.11.2Prevention of Climate Change
2.11.3Adaption to Climate Change
3.Energy-Conscious Planning and Zoning
4.Methods of Information Acquisition for Planning (Measurements, Wind Tunnels, Numerical Modelling)
5.Climatic and Air Hygiene Maps as Aids for Planning and Zoning (Example: Climate Atlas Federation Region Stuttgart)
6.Recommendations for Planning
7.Bibliography
8.Thematic Websites
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CHARACTERISTICS AND FORMS OF THE URBAN CLIMATE
   
 2.2 Urban Heat Budget

In contrast to the open landscape, the balance of energy – which is largely determined by shortwave radiation from the sun and by the longwave emanation of warmth – in a city is substantially altered. The relative influences on the urban heat budget are depicted schematically in Figure 2/2 (ROBEL et al, 1978). Solar radiation (dispersion and absorption) is reduced by particulate matter (pollutant gases and aerosols) in the city atmosphere. In the ultraviolet spectrum, the reduction ranges from 5% in summer up to 30% in winter. Global radiation (both direct solar radiation and diffuse celestial radiation) can be up to 20% less in cities. The duration of daily sunshine is further lessened up to 15% (LANDSBERG, 1981).

Soil capping and the correspondingly smaller proportion of green space reduces evaporation, contributing to increased temperatures in the city.

The built mass of the city accumulates heat from the incoming solar radiation, which indicates that daily maximum temperatures occur later in the day and that the temperature fluctuation range is narrower in a city versus in the surrounding land Fig. 2/3) (BRÜNDL et al, 1986) (Fig. 2/3a). The buildings release the stored heat only slowly overnight, and are still relatively warm in the morning.

Energy transfers in a city occur in large part not at ground level, but rather in the area of the roof level and the upper floors of buildings.

The effective dispersal of radiation is reduced by the relatively high proportion of pollutant gases (e.g. carbon dioxide), which can absorb longwave heat radiation and can thus lead to a warming of the city atmosphere – the local greenhouse effect.

A factor that can"t be neglected in urban areas is the anthropogenic heat generation inducing an additional warming particulary in winter during the heating period. It depends on the population density as well as the per capita consumption. The annual urban average in Central European cities is 30 W/m² (KUTTLER, 2010).

 
 
 
Fig. 2/2: Measured variables for the urban heat budget (from ROBEL et al., 1978)
 
Fig. 2/3: Diurnal variation of the air temperature in Berlin, Source: Leibniz-Institute for regional geography 2003
 
Fig. 2/3a: Differences in temperature between the Munich central city and the surrounding land in August and December 1981 (BRUENDL et al., 1986)