Journal of Wind Engineering and Industrial Aerodynamics
Prediction of wind environment and thermal comfort at pedestrian level in urban area
Introduction
The world's urban population was 2.9 billion (47.2%) in 2000 and is expected to rise to 5 billion (60.2%) by 2030. During 2000–2030, the world's urban population is projected to grow at an average annual rate of 1.9% (World Urbanization Prospects, 2001). In line with the rapid urbanization and growth of urban population, there are increasing concerns regarding the quality of urban environment. In this respect, urban thermal environment is one of the major concerns, which had lead to numerous researches on this topic. The urban thermal environment has been worsened by the Urban Heat Island (UHI) effects. The UHI is now regarded as one of the most serious urban environmental problems in the world. The contributing factors of UHI include less vegetation in city area, absorption of solar energy input by concrete and paved surfaces, multiple heat reflections from canyon structures of high-rise buildings, anthropogenic heat releases from air-conditioning systems, automobiles, etc. In order to reduce the UHI effects, various mitigating measures have been proposed. The most commonly applied is tree planting. The monetary benefits of urban trees are difficult to quantify because these trees can provide numerous private and public benefits. The latter includes improving thermal environment, reducing air pollution and community noise problems, enhancing biodiversity and meliorating aesthetics (Akabari et al., 1992; McPherson and Rowntree, 1993; Rowntree, 1989). Thus, the existence of tree covered ground surface is one of the most essential factors to be considered in urban design. Accurate reproduction of aerodynamic effects of trees is also very significant for predicting wind environment in urban area.
Wind environment is one of the most important factors to be considered in UHI study as it has significant influence on UHI effect and outdoor thermal comfort. The conventional urban wind environment assessment methods only took into consideration the influence of topographic features and geometry of buildings (cf. Fig. 1(1)). These methods may be inadequate to reflect the real conditions of city where there are objects of various scales within the street canyons. Stationary objects (cf. Fig. 1(2)) such as trees and telephone boxes, and non-stationary objects (cf. Fig. 1(3)) such as moving vehicles and swinging hanging-signboards (commonly seen in Asian countries), may alter the surface roughness to certain extent. In order to obtain accurate quantitative data for urban wind environment assessment, these objects must not be overlooked. In recent years, canopy models for reproducing the aerodynamic and thermal effects of trees, buildings and automobiles have been developed and applied to various problems related to urban climate. The canopy models were incorporated into the meteorological mesoscale models. The simulation methods for mesoscale and microscale climates were then integrated into the total simulation system using the nested grid technique.
The growth of CWE applications in the past decade had greatly expanded the scope of wind engineering. Now the application of CWE ranges from the microclimate around a human body to the mesoscale climate in urban area. The aims of this paper are to present the progress of CWE researches for predicting pedestrian level wind environment around buildings primarily achieved by the researchers in the field of environmental engineering in Japan, together with a brief review on turbulence modeling for CWE applications to problems related to wind environment and cross comparison of predicted results with various turbulence models for several test cases, and to demonstrate the significant effects of stationary and non-stationary objects (tree canopy and vehicle canopy, respectively) on turbulent diffusion process within street canyons.
Section snippets
Appearance of dynamic SGS models and their applications in wind engineering
The standard Smagorinsky model was widely used in the computation of LES in the CWE researches conducted in the early period. In the Smagorinsky model approach, a simple eddy-viscosity type approximation is used to simulate the subgrid scale (SGS) stress τij in SGS. The SGS eddy viscosity, νSGS, is estimated bywhere is the filtered quantities, the grid-filter width, fμ the wall damping function.
In the standard
Various SGS obstacles in real situations
The real situations of environment in street canyons are influenced by the interaction of various objects, both stationary and non-stationary. In most of the previous CFD simulations of flow around buildings, only the influences of topographic features and building geometry were considered (cf. Fig. 1(1)). At the pedestrian level, influences of small obstacles such as trees (stationary) and automobiles (non-stationary) are significant (cf. Figs. 1(2) and (3)). Their effects have been neglected
Integration of CWE simulations with various scales
CWE applications now cover various phenomena, at scales ranging from microclimate around a human body to regional climate (cf. Fig. 13). Although scales associated with these phenomena are different, they are related and coupled to each other. Research efforts, thus, should be devoted to develop a method for integrating the submodels into a comprehensive, total simulation system. For this purpose, it is necessary to develop a new software platform which not only can handle many subsystems for
Concluding remarks
This paper reviewed the progress in CWE research over the past 10 years, primarily achieved by the researchers in the field of environmental engineering in Japan. The first part of the paper outlined the progress in turbulence modeling for predicting turbulent flow around buildings and wind environment in building complex. In the 1990s, many investigations were carried out to examine the performance of the dynamic LES models based on the dynamic Smagorinsky type, DM type, Lagrangian dynamic
Acknowledgments
This paper reviewed the recent progress in CWE applied to environmental problems. Many topics included in this report are the results of collaborations extended over years with Prof. S. Murakami (Keio University), Prof. Y. Tominaga (Niigata Institute of Technology), Prof. R. Ooka (IIS, University of Tokyo), Dr. S. Iizuka (National Institute of Resources and Environment), Prof. S. Yoshida (Fukui University), Dr. K. Kondo (Kajima Corporation), Dr. K. Sasaki (Shimizu corporation) and Dr. T.
References (110)
- et al.
A new turbulence model for predicting fluid flow and heat transfer in separating and reattaching flows—II. Thermal field calculations
Int. J. Heat Mass Transfer
(1995) On the k–ε stagnation point anomaly
Int. J. Heat Fluid Flow
(1996)Modelling of turbulent flows within plant/urban canopies
J. Wind Eng. Ind. Aerodyn.
(1993)- et al.
Performance of various sub-grid scale models in large-eddy simulation of turbulent flow over complex terrain
Atmos. Environ.
(2004) - et al.
Large-eddy simulations of turbulent flow over complex terrain using modified static eddy viscosity models
Atmos. Environ.
(2006) - et al.
Generation of velocity fluctuations for inflow boundary condition of LES
J. Wind Eng. Ind. Aerodyn.
(1997) - et al.
Calculation of the flow past a surface-mounted cube with two-layer turbulence models
J. Wind Eng. Ind. Aerodyn.
(1997) - et al.
Numerical simulation of flow over topographic features by revised k–ε model
J. Wind Eng. Ind. Aerodyn.
(2003) Optimization of roughness parameters for staggered arrayed cubic blocks using experimental data
J. Wind Eng. Ind. Aerodyn.
(1993)- et al.
CFD analysis of mesoscale climate in the Greater Tokyo area
J. Wind Eng. Ind. Aerodyn.
(1997)