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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
   
 2.3 Urban Heat Islands

With regards to temperature, cities contribute constantly to warming; this, however, is not necessarily a negative characteristic of the urban climate. On average, cities are annually 1 to 2 degrees Celsius warmer than their surrounding landscapes. Particularly large temperature differentials arise on clear nights during the daily temperature minimum.
(MATZARAKIS et al., 2008; KUTTLER, 2011).

Figure 2/4 shows this relationship for European cities dependent upon on the size of the city. Cities with millions of inhabitants can witness a temperature differential above 10 degrees. One can also discern, however, a recognizable heat island effect throughout the smaller cities.

Studies in Munich (BRÜNDL et al, 1986) have shown that temperature levels in city districts depend largely upon the degree of soil capping. An increase of 10% in the proportion of soil capping thus produces a rise in average annual temperatures by 0.2 degrees.

For every 10% increase in the degree of capping, the long-term average level of the air temperature in the built area (following completion of all construction activity) rises approximately 0.2 degrees Celsius above the temperature of the non-built surroundings. In sunny weather conditions, for every 10% increase in the degree of capping the daily average temperature rises 0.3 to 0.4 degrees, the average daily maximum rises 0.3 degrees, and the average daily minimum rises 0.5 to 0.6 degrees Celsius ( Figure 2/5).

This generally higher temperature level exerts a perceptible positive effect on the inner-city vegetation. The effect can be noted by the presence of numerous warmth-loving plant types in front yards and parks as well as in the lengthened vegetation period. Opportunities for outdoor activities are also more frequent in cities. Similarly, the need for heating energy is reduced.

Various types of ground cover warm themselves at highly different rates on cloudless summer days with little wind. This depends on the absorption ability, the heat capacity, the heat conductivity, and the evaporation ability of the underlying ground.

For example, asphalt absorbs 80% to 90% of incoming radiation, whereas a white wall absorbs only 20% to 35%. Temperature measurements vary between less than 30 degrees to almost 50 degrees Celsius (LORENZ, 1973).

The diurnal variations in the temperatures of various materials and surfaces on a hot summer day are shown in Figure 2/6 from FEZER (1975).

In addition to the material properties of surfaces, the height and arrangement of buildings is relevant to the temperature conditions in a city. Narrow streets and alleys produce shadowing effects, which leads to a delay in the warming of the urban realm. The artificial narrowing of the horizon also decreases the heat dissipation of the building surfaces, however, which reduces nightly cooling in the streets.

The interaction of these factors inside the various structures and built densities of the city leads to a mosaic of varied thermal microclimates, which join with each other to produce a clearly-defined heat island (or heat archipelago) when compared with the surrounding land. These heat island conditions are recognizable in infrared heat images (z. B. Thermal map, Stuttgart Region, Chapter 5/2) with their large spatial differentials in surface temperatures.

The development of heat islands in Stuttgart is shown also in the following representation (Figure 2/7) and (Figure 2/7a) of temperature distributions on 21 August 1965 at 6:00 AM (HAMM, 1969). The figure shows the heat island effect in summer; according to the same study, however, the heat island effect is of the same order of magnitude in winter. The large temperature differentials in Stuttgart amount to roughly 6 degrees between the central city and the edge zones of the city basin

Against the background of global climate change and the need to adapt to inevitable climate change portion of the urban heat island has become the subject of numerous research projects (e.g. EU project UHI , 2011 - 2014).

 
 
 
Fig. 2/4: Maximum temperature differentials for European cities
 
Fig. 2/5: Regression relationship of the proportion of capped ground and temperature, Source: BRUENDL et al. (1986)
 
Fig. 2/6: Temperatures of various surface materials on a midsummer day (from FEZER, 1975)
 
Fig. 2/7: Temperature distribution in the Stuttgart central city on 21.8.1965 at 06:00 (HAMM, 1969)
 
Fig. 2/7a: Temperature distribution in the Stuttgart central city on 16.1.1966 at 22:30 (HAMM, 1969)
 
Abb. 2/7b: Temperature distribution in Tokyo on 01.03.1999 at 21:00