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1.Climate as a Public Interest in Planning and Zoning
2.Characteristics and Forms of the Urban Climate
3.Energy-Conscious Planning and Zoning
4.Methods of Information Acquisition for Planning (Measurements, Wind Tunnels, Numerical Modelling)
4.1Measurements
4.1.1Stationary Measurements
4.1.2Measurements with mobile measurement devices
4.1.3Tracer Experiments
4.1.4Vertical Soundings
4.2Wind Tunnel
4.2.1Overview
4.2.2Operation and Investigation Methods
4.2.2.1Visualization of flows and pollutant dispersion by smoke
4.2.2.2Wind Velocity Measurements
4.2.2.3Measurement of Concentration Distribution in Dispersal Experiments
4.2.3Locations of Wind Tunnels
4.3Numerical Modelling of Flow and Transport Processes
4.3.1The Wind Field Model DIWIMO
4.3.2The Cold-Air Flow Model KALM and KLAM 21
4.3.3The Model STREET for Estimating Traffic-Produced Pollution
4.3.4The Model MLuS-02 for Calculating Pollutant Dispersal
on Roads Without Dense Peripheral Development
4.3.5The Model PROKAS for Calculating Air Pollution on Roads
4.3.6The Micro-Scale Model MISKAM
4.3.7Mesoscale Terrain Climatic Models
4.3.8The Urban Climate Models RayMan , ENVI-met and MUKLIMO_3
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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METHODS OF INFORMATION ACQUISITION FOR PLANNING (MEASUREMENTS, WIND TUNNELS, NUMERICAL MODELLING)
   
 4.2.1 Overview

The requirements for the identification and illustration of environmental impacts in the field of urban land use planning have continuously increased, not least because of changes within the Federal Building Code (BauGB). For one thing, this might be due to people"s growing consciousness for environmental issues, for another it is the settlement becoming denser and denser in Germany , which forces conflictual uses closer together.

Increased requirements have sometimes led to costlier and more time-consuming examination methods, especially when material losses or damages are at stake. One of these methods is the use of a wind tunnel in the planning stage.

The following issues can principally be analysed and quantified in a wind tunnel:

  • a modification of the large-scale aeration within the planning area and its surrounding
  • a modification of the small-scale dispersion of pollutants or smells due to buildings
  • a modification of the wind comfort due to intended building projects
Wind tunnel experiments also help to illustrate flow and dispersion patterns in a more descriptive way for the use in committees or other decision-taking bodies.

Typical fields of application are:
  • the prevention of disturbing wind flows around tower blocks
  • the effect of squares and roads on the aeration of urban areas
  • the reduction of snowdrifts at roads or the migration from heaps
  • the positioning of external air inlets for air conditioning systems
  • the propagation of smells from commercial enterprises, landfills and factory farms
  • the dispersion of emissions in the case of disturbances
The size of the area under investigation ranges from some metres (local wind comfort) to several kilometres (aeration of urban areas), depending on the topic.

Criteria for the assessment of wind comfort refer to either the average hourly value of the wind speed (Table 4/1) or the gust wind speed (Table 4/2). In the VDI is in progress - Directive 3787, Part 4 " methods to describe strong and weak winds in built-up areas and their evaluation " is an attempt to formulate a unified assessment methodology.

Wind velocity (m/s)

Effect

to approx. 1.5

calm, no noticeable air flow

approx. 1.6 - approx. 3.3

in the face perceptible air flow

approx. 3.4 - approx. 5.4

wind moves light flags

approx. 5.5 - approx. 7.9

paper flies up, hair-style is destroyed

approx. 8.0 - approx. 10.7

wind force at the body clearly noticeably

approx. 10.8 - approx. 13.8

to use umbrellas with trouble

approx. 13.9 - approx. 17.1

difficulties when going


Table 4/1: Connection between wind velocity and wind effect upon humans (from STIEMER, 1977)

Gust wind velocity

Excess frequency

Evaluation criteria

< 6 m/s

> 6 m/s

-

max. 5%

no wind comfort problems permissible in parks, waiting ranges, road cafes, on playgrounds

> 6 m/s

> 15 m/s

max. 20%

max. 0.05%

permissible on surfaces for brief stay (less strict criterion), and/or which are fast exceeded

> 8 m/s

max. 1%

permissible within waiting and seat ranges

> 10 m/s

max. 1%

permissible on surfaces for brief residence time (strict criterion)

> 13 m/s

max. 1%

permissible at corners of a building, permissible for problem-free running

> 13 m/s

> 1%

unpleasantly, annoyingly, wind protection

> 18 m/s

> 1%

danger


Table 4/2: Criteria for evaluating the wind conditions for a specific object, Source: LOHMEYER et al., 1992