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Sustainability 2018, 10(1), 206; https://doi.org/10.3390/su10010206
Assessing the Effects of Urban Morphology Parameters on Microclimate in Singapore to Control the Urban Heat Island Effect
School of Architecture, Harbin Institute of Technology, Heilongjiang Cold Region Architectural Science Key Laboratory, No. 66 Xidazhi Street, Nangang District, Harbin 15001, China
Department of Building, National University of Singapore, School of Design and Environment, 4 Architecture Drive, Singapore 117566, Singapore
Author to whom correspondence should be addressed.
Received: 25 December 2017 / Accepted: 11 January 2018 / Published: 16 January 2018
It is important to alleviate the “heat island effect” in urban areas, especially tropical cities. Microclimate is normally affected by the urban morphology parameters. The objective of this work is to investigate the correlation between air temperature variations and urban morphology parameters in tropical cities. Field measurement was carried out to record the air temperature at 27 points within an 8 km2 urban area continuously in Singapore for one year. Geographical information system was applied to extract the urban morphology parameters. Generally, the maximum and minimum air temperature spatial differences in the study area ranged from 3.2 to 6.5 °C, indicating the significant effects of urban morphology on the air temperatures. Based on the fitting results of created multilinear regression models, parametric study has been performed to investigate the specific effects of urban morphology parameters on air temperatures. This work has proposed a much more precise regression model to predict the air temperature with various urban morphology parameters. In addition, meaningful value of reference has been offered for urban planners and landscape designers to effectively control the air temperature in tropical cities such as Singapore.
Keywords:urban heat island effect; air temperature; microclimate; urban morphology parameters tropical city
The urban heat island (UHI) effect is one of the most severe problem in tropical cities. As the population grows, building density also increases resulting in distinctive surface energy balance and microclimatic characteristics at the local scale [1,2]. The local climate of an urban area may be substantially affected by landscape factors as well as geometrical characteristics, anthropogenic activities, and heat sources present in the area. The urban environment continually shapes the microclimate in numerous ways . There is a mounting research interest in microclimate issues, as they represent important factors in achieving sustainability inside cities, which serve increasingly large populations across the globe. The urban microclimate both influences and is influenced by human behavior and decision-making, due to the complex interactions between air temperature, relative humidity, wind speed, and micro-scale landscape parameters [4,5,6]. Empirical knowledge of local air temperature variability and the relationship between the microclimate and artificial impact factors is critical in adapting the urban climate to changes in its thermal environment.
Outdoor spaces are important parts of any urban area as they provide thoroughfares for pedestrian traffic as well as venues for outdoor activities. Increased outdoor activity in urbanized areas has a wealth of positive effects on the population. Outdoor spaces must be properly designed for maximum benefit to the urban dwellers who enjoy them. The outdoor microclimate is an important factor in the quality of an urban outdoor space, as it affects thermal comfort throughout all aspects of outdoor activities.
The microclimate is influenced by many factors. As reported within a 50-m radius, critical parameters with significant influence on the minimum temperature (Tmin) and average temperature (Tavg) values include the green plot ratio (GnPR), total tree leaf area (TREE), and percentage of green area (GREEN); parameters with significant influence on the maximum temperature (Tmax) are sky view factor (SVF), GnPR, TREE, and GREEN . Parks have significant cooling effect upon nearby buildings, and the distance from the nearest park can affect the ambient temperature in a given area [8,9,10]. As the cooling effects of vegetation or water extend into the surroundings, a park can reduce the air temperature in a busy commercial area by up to 1.5 °C .
Urban geometry and the thermal properties of urban surfaces are also important parameters influencing the urban climate [12,13,14,15]. The local urban context is made up of buildings, roads, trees, and lawns; land cover features represent various ratios of buildings and vegetated areas. Sun  found that air temperature is significantly correlated with green ratio and building ratio during night hours in Taiwan. Yan et al.  reported that increasing the percentage of vegetation cover can significantly decrease air temperature, while increase in building area significantly increases air temperature according to field measurements taken in Beijing. Yokobori  found that air temperatures vary significantly according to ambient land cover types; air temperatures decrease as the amount of vegetated area around various measurement sites in Japan increase. Sky view factor (SVF) is another crucial factor affecting mean radiant temperature (Tmrt) which can change with site geometry. When an urban space has high SVF condition, it means more solar radiation reaches the ground below during the daytime. The opposite phenomenon occurs at night, forming an “urban cool island”. Interestingly, however, some studies have shown that SVF has very little impact on air temperature [19,20].
Urban microclimates are a formed via a highly dynamic and complex process which varies within different macroclimate. In addition, due to the differences registered in the thermal perception of different populations, it is necessity to perform study aimed at evaluating the microclimate of a specific city or site [21,22]. According to previous studies, the main microclimate parameters affecting any open space include land cover, site geometry, and spatial location (e.g., proximity to parks or water bodies). Previous researchers have simulated and conducted field measurement on these parameters extensively, but most studies center around single-parameter models—researchers tend to examine one problem from different respective angles corresponding to different respective landscape parameters, which makes it very difficult to conclude which particular landscape factor most significantly affects air temperature within the urban context. In addition, urban climates are affected by external factors such as the topographic features, season, and prevailing weather. It is important to control for geographical, seasonal, and meteorological (e.g., wind speed and cloud cover) variables as much as possible to determine the location-specific changes in urban air temperature.
The purpose of this study can be summarized as follows.
- Continuous field measurement at 27 points in the studied area to collect the microclimatic weather conditions at 2.5-m height for one year to investigate the spatial and temporal microclimate parameters related to the distribution of open space at the local scale in Singapore, and explain changes in microclimate within this specific morphology.
- Determine the relationship between urban morphology parameters and microclimate parameters, as well as the influence radius of the surrounding urban morphology parameters.
- Develop empirical models to correlate the air temperature at 2.5-m height with the urban morphology parameters and weather parameters.
2.1. Study Area
The Köppen Climate Classification subtype for Singapore climate is “Af” (Tropical Rainforest Climate). Near-surface air temperature usually ranges from 23 °C to 32 °C. April and May are the hottest months, and the monsoon season extends from November to March . The mean annual trends of climate has been summarized in Table 1.
Singapore is a garden community with no distinct border lines between urban and rural areas. Its street canyon layout differs from other cities in regards to its distinctive landscape elements . We took field measurements in the Jurong Lake area (Figure 1) to establish a working understanding of how the landscape factors impact the ambient environment in Singapore. Jurong East is a residential town representative of the traditional Singaporean street canyon layout. We selected 27 different measurement sites across the study area to ensure a sufficiently wide range of SVFs, building plot ratios, and vegetation cover rates in investigating the quantitative relationship between microclimate parameters and landscape (Figure 2). The research area is very flat, so any temperature difference due to topography was negligible. The measurement sites located are sufficiently close to one another to be affected by uniform meso-scale climate conditions, yet also affected by distinctly different micro-scale landscape characteristics.
2.2. Microclimate Parameter Measurements
Mobile traverse measurements may be affected by error during the test process. It may be challenging to secure sufficient data for real environment microclimate parameter analysis due to such error. We used fixed rather than mobile microclimate stations to conduct measurements from August 2016 to June 2017. Each microclimate station was assembled as shown in Figure 3; the precision of each sensor is listed in Table 2. The steel beam direction was set from west to east to obtain accurate wind direction information. Records were taken in 5 min intervals. Every two weeks, we downloaded the data and changed the sensor batteries. We manually recorded windy, rainy, and cloudy conditions from the ground to investigate different factors influencing the UHI.
2.3. Weather Data Selection for Analysis
The data obtained including air temperature, humidity and wind speed is authentic when the weather conditions are clear and sunny. Therefore, during the measuring period rainy and cloudy days were excluded while clear and sunny days are selected for data analysis and model development. The criterion requiring bell-shaped hourly solar radiation and air temperature profiles was proposed to select analyzed days.
- Daily maximum solar radiation larger than 900 W/m2;
- Hourly temperature and hourly solar radiation take on a bell shape profile;
- Daily average temperature higher than 24 °C; and
- Daily average wind speed less than 3 m/s.
According to the criterion described above, 50 typical days have been selected. The selected days have been randomly divided into two groups, which were used for model development and validation, respectively. As shown in Table 3, 40 days were selected for model development and 10 days were selected for the validation.
2.4. Urban Morphology Parameter Measurement and Computation
Numerous parameters are available to assess and quantify the effects of urban environment characteristics on air temperature [25,26,27,28]. However, the Singapore island temperature pattern shows urban heat island characteristics based on the conditions of surrounding buildings, greenery, and pavement . We selected parameters under four main principles: (1) they have potential effects on microclimate; (2) they are easily calculated; (3) they are easily controlled by design; and (4) they have minimal redundancy. In this study, we selected three categories of urban morphology parameters including land cover features, site geometry, and spatial location to measure site environmental characteristics. The land cover features include green plot ratio (GnPR), building plot ratio (BPR), percentage of pavement (PP). (The “plot ratio” is the ratio of the total floor area to the total selected land area.) The site geometry includes sky view factor (SVF) and the spatial location include distance to park (DP) and distance to water (DW). Site geometry was measured using SVF and spatial location was measured according to distance to the nearest park and water body. Our main analysis tool in developing the climatic maps was the Geographical Information System (GIS), a technology to view and analyze data from a geographic perspective. GIS links the location and information layers to reveal how they interrelate. The variation in air temperature with regard to the land cover composition of each measurement site was quantified after establishing a buffer zone with 20 m, 50 m, or 70 m radius in this study.
We controlled the variables to fully ensure that every test point provided meaningful information. We used two different SVF calculation methods. For 20 m radius, we used an 8mm circular fisheye lens to obtain images which were imported to the Rayman model ; for 50 m and 70 m radii, we used GIS (ESRI, Redlands, CA, USA)  to obtain the calculations shown in Figure 5g. The effects of parks and water bodies were estimated based on the straight distance between each measurement site and the edge of the park or water body nearest to the site.
The mean radiant temperature is one of the meteorological parameters that can influence human energy balance and human thermal comfort . The global temperature represents the weighted average of radiant and ambient temperatures. If the global temperature, air temperature, and air velocity are known, then Tmrt can be calculated according to Equation (1) :where:
- Tg = Globe temperature (°C)
- Va = Air velocity (m/s)
- Ta = Air temperature (°C)
- D = Globe diameter (mm)
- ε = Globe emissivity
We performed greenery mapping using the Green Plot Ratio (GnPR) method, as developed by Ong (2003). GnPR is derived from the average amount of greenery on a given lot per the leaf area index (LAI) in proportion to the total lot area. It is the sum of the products of the area of each greenery type and its corresponding LAI value, which is divided by the total lot area. The GnPR equation is as follows :where:
- LAIn: leaf area index of species n
- An: canopy area of species n
- nn: number of plants of species n on the site
The values of DP and DW were obtained by GIS. The description of each test point is shown in Table 4.
2.5. Regression Analysis for Model Development
Multiple regression analysis was carried out to determine how well the observed air temperature differences could be explained by the combination of the six urban morphology variables (Table 4). The regression results offer insight into the influence of different variables on air temperature at different points in time. The coefficient of determination (R2) represents the proportion of the variation in air temperature that could be explained by the regression models; the standardized coefficients (Beta coefficients) of predictive models represent the relative contributions of different landscape variables to the air temperature difference. The calculation radius has a strong influence on BPR, GnPR, and PP; different areas have different influence radii .
In a similar study on Curitiba, Kruger found that 56 m of the calculation radius had the most significant impact on temperature variation among 56 m, 125 m, and 565 m radii . In Beijing, Yan found that 75 m is the most significant radius . The most significant radius in Singapore remains unclear, so we chose three radii to test the calculation impact on urban microclimate by comparison.
We used a multivariate regression analysis to quantify the relative contribution of six landscape variables to differences in air temperature. The predictive model is:
Y = a + b1BPR + b2GnPR + b3SVF + b4DP + b5DW + b6PP
3. Results and Analysis
3.1. Correlation between Air Temperature and Urban Morphology Parameters
Table 5 shows the significance of six urban morphology parameters with three calculation radii. During daytime hours, 83.2% of the air temperature data could be accurately predicted by the six parameters when the calculation radius is 20 m, 91.7% for 50 m and 87.4% for 70 m, respectively, According to the R2 values, the 50-m radius has the most significant impact on temperature variation in Singapore. The Beta coefficients indicated that among all six parameters, SVF is the most significant parameter. According to this model, 10% increase of SVF would lead to an increase of air temperature by 0.21 °C when the radius is 50 m. When calculation radius becomes wider, BPR becomes another important impact factor; the air temperature decreased by 0.13 °C when BPR increased to 10%. The negative coefficients of GnPR and BPR suggest that an increase in green plot ratio and building plot ratio would decrease the air temperature. By contrast, the positive coefficients of SVF, DP, and DW altogether indicate that temperature would increase with increased distance from parks or water bodies, although which significances are relatively smaller.
The six urban variables can explain the daytime temperature variables much better than nighttime. During nighttime hours, 67% of the air temperature data could be accurately predicted by the six parameters when the calculation radius is 20 m, 67.7% for 50 m and 64.2% for 70 m, respectively. SVF is the most significant parameter for all calculation radius. A 10% increase in SVF decreased air temperature by 0.14 °C, 0.17 °C, and 0.08 °C respective to the three radii we tested. The negative coefficients of GnPR and SVF suggest that an increase in green plot ratio or SVF would decrease air temperature. By contrast, the positive coefficients of DP and DW indicate that temperature would increase with increasing distance from parks or water bodies.
Based on the measured data on selected days listed in Table 3, Equations (2)–(6) were developed to predict Tavg-day, Tavg-night, Tavg, Tmax and Tmin, respectively. Equations (2) and (3) show that Tavg is correlated to daytime and night average temperature at meteorological station (Ref Tavg-day), the minimum relative humidity (RHmin) and average wind speed (WINDavg).
Tavg-day = 2.31 + 0.778RefTavg-day − 0.11RHmin(%) − 0.341WINDavg
(R2 = 98.7, F = 9815.39, Standard Error = 0.51)
(R2 = 98.7, F = 9815.39, Standard Error = 0.51)
Tavg-night = 0.57 + 1.11RefTavg-day − 0.67RHmin(%) − 0.228WINDavg
(R2 = 92.1, F = 9134.51, Standard Error = 0.55)
(R2 = 92.1, F = 9134.51, Standard Error = 0.55)
Equations (5) and (6) show the relationship between the air temperature and urban morphology parameters. Tmax appears during daytime and Tmin appears during nighttime.
Tmax = 2.97SVF − 0.003GnPR − 0.019BPR − 1.13E-5DP − 1.112E-5DW + 1.76PP + 28.57
(R2 = 91.7, F = 8814.31, Standard Error = 0.322)
(R2 = 91.7, F = 8814.31, Standard Error = 0.322)
Tmin = −0.706SVF − 0.014GnPR + 0.026BPR − 2.45E-5DP + 0.6E-5DW + 0.026PP + 28.894
(R2 = 77.7, F = 12991.11, Standard Error = 0.33)
(R2 = 77.7, F = 12991.11, Standard Error = 0.33)
Equations (3)–(6) were validated against the measured temperatures, as listed in Table 3. Figure 4 has illustrated the deviations between the predicted and measured Tavg-day, Tavg-night, Tavg, Tmax and Tmin, respectively. In the box plot, the black line in the middle of box is the median temperature difference values. The bottom and top of box indicate the 25 and 75 percentage, respectively. The values between the five predicted and measured temperatures are all close to 0 °C. Overall, 96% of the values fell in the range of −1 °C to 1 °C (region of shallow green), while 54% of fell in the range of −0.5 °C to 0.5 °C (region of dark green). In addition, the accuracies of these estimations were evaluated by the index of normalized root mean square error (NRMSE) using Equation (7), which is defined as the ratio between the root mean square error RMSEi (calculated from predicted temperature) and RMSEi=ref (calculated considering that each station is at the reference temperature value) .
3.2. Influence of Temporal and Spatial Variation on Microclimate
Figure 5 shows the changes in temperature and RH as time during the whole day period for each measuring point. The spatial patterns of the microclimate parameters are shown in Figure 6. In addition, the daytime data in Figure are the average data at 14:00, while the nighttime data are at 02:00 from clear days in June, July and August 2017. Figure 5 also shows where the air temperature and RH differences among different locations were very significant. During the day, the max air temperature difference between the lowest Point (12) and highest Point (19) at the same time reached up to 6.5 °C. RH differed by 15% between the lowest Point (20) and highest Point (12).
The trends for temperature rose sharply at every test point with time from 08:00 to 14:00, then fell to a smooth interval until 08:00 the following day. The hottest place was at Point (20), which had mean air temperature of 37.2 °C. This site is located in an open space with grass cover but without any shading and is fully exposed to solar radiation during the day. Though the transpiration of greenery can reduce air temperature, shading is a much more important factor in tropical cities. The lowest temperature appeared on Point (7), which has the lowest SVF. As shown in Figure 6a, the test points with lower temperatures are all located in the center of the commercial area despite the high anthropogenic heat flux also present in this area. The shading from trees and high plot ratio of buildings appears to stave off the continuous heating of the pavement surface by solar radiation.
The distribution of Tmrt is slightly different from the temperature distribution due to the differing albedo among different interfaces (Figure 6e). Besides, Tmrt increases as SVF, which is discussed in detail in the following section. The distribution of Tmrt has a significant correlation with SVF (Figure 6g). During the daytime, RH increases slightly with DW, however, not significantly. The RH distribution during the nighttime period is opposite to that during the daytime period (Figure 6c,d). The RH near water was also higher than in other areas throughout the study period (Figure 6d). In the building area, the RH is almost uniform. During nighttime, the temperature distribution pattern in the study area becomes especially clear (Figure 6b). The park areas are transformed into cool islands surrounded by hot areas. The mean air temperature difference between the lowest point inside the park and the highest point in the building area reached 4.3 °C. The high BPR and low SVF make heat less easily dissipated by winds moving through the area (Figure 6f).
3.3. Influence of Site Geometry Parameter on Microclimate
SVF is the most important factor impacting air temperature in tropical cities as previous report . During the daytime, air temperatures in our study area increased with increasing SVF (Figure 7a). Less “sky openness” resulted in lower air temperatures under the effects of solar radiation. According to the statistical measurements we obtained, about 59% (p < 0.001) of the open space variations in air temperature can be explained by the variations in SVF during the daytime. Conversely, this correlation was negative during nighttime hours—at night, the net outgoing long-wave decreased at locations with low SVF values, resulting in higher temperatures (Figure 7b). SVF also can explain 15% of air temperature variation during the night.
Open space with less vegetation has a very high daytime air temperature due to the maximum solar heat gain received by the ground surface. Air temperature is quite cooler at night because the heat is released to the atmosphere without any entrapment by the surrounding buildings. On the contrary, sites dense with buildings and surrounded by little vegetation, heat accumulates during the day due to the lack of greenery but is not easily released due to the heat capacity of the surrounding buildings.
Vegetation reduces the sky openness in an urban environment. During the day, we observed a significant and close correlation between SVF and air temperature (R2 = 0.59, p < 0.001). In general, higher SVF yields higher air temperature. Larger open areas receive more solar radiation, which leads to a higher air temperature. Trees reduce the level of sky openness (i.e., provide shading), thus, they cool the air temperature. At night, we observed a weak correlation between SVF and air temperature (R2 = 0.15, p = 0.04). There is no adverse impact (i.e., reduction of nighttime net long-wave loss) due to the reduction of SVF by trees in the study area.
3.4. Influence of Land Cover Parameters on Temperature
The 50 m radius best explained the temperature variables, so we focused on this radius in our subsequent analysis of the relationship between the land cover features and microclimate. The land cover composition affects air temperatures differently at different time points, as shown in Figure 8. During daytime hours, there was a negative correlation between air temperature and BPR (Figure 8a; R2 = 0.31, p = 0.002) but a positive correlation between them at night (R2 = 0.13, p = 0.06). When the BPR reached 5.6, temperature was balanced due to the corresponding low SVF. As indicated by Figure 8b, no obvious correlation exists between wind speed and BPR, which is due to that wind speed is rather random and normally associated with the architectural composition as well as vegetation. However, it could be deduced from Equations (3) and (4) that the wind speed has certain correlation with the Tavg-day. In Figure 8c, it is shown that vegetation reduced the temperature during daytime hours, or rather each 10% increase in GnPR decreased temperature by 0.3 °C (daytime: R2 = 0.47, p < 0.001). During nighttime, however, this relationship was less significant (nighttime: R2 = 0.18, p < 0.017). Other similar studies in Beijing and Tokyo actually showed phenomena opposite to the ones in this work [17,18]. In terms of vegetation, the LAI index of trees specifically (as opposed to shrubs or grass) provides shading which mitigates the effects of solar radiation; the transpiration of greenery can also reduce air temperature. Within the markedly complex urban context, however, GnPR is not the main factor controlling the air temperature. Even with high percentage of vegetation cover, the temperature does not easily change without shading because solar radiation makes the greenery less able to perform transpiration. Plants in Singapore have relatively high LAI index, i.e., better cooling effects than plants in colder regions. As shown in Figure 8d, we also found no significant relationship between RH and GnPR in either day or night (R2 = 0.05, p = 0.21; R2 = 0.02, p = 0.71).
3.5. Influence of Spatial Location Parameters on Temperature
Figure 9a,c shows the relationships between air temperature with DP or water DW, respectively. During nighttime hours, air temperature increased with increasing distance to the nearest park, indicating that this variable (distance to park) accounted for 28% of the variance in the air temperature distribution. However, there was no such significant relationship between air temperature and distance to park during the day (R2 = 0.08, p = 0.13). The air temperatures determined by the distance to water variable were similar: R2 values were 0.12 and 0.32 during daytime and nighttime, respectively. No significant correlation exists RH and distance to water during the day.
Our remote sensing results reflect sizable spatial differences in temperature across the study area. The magnitude and spatial characteristics of these differences varied depending on time of the day. At night, the pattern of temperature distribution in the study area was very clear. Park areas became cool islands surrounded by hotter building areas. The spatial pattern formed in daytime hours tended to be less well-defined. Daytime air temperatures in high-rise building areas were occasionally cooler than those in the park sites, resulting in some urban cool islands. Similar phenomena were observed by Chow and Roth , which are attributed to the slower warming of urban surfaces due to the solar heat storage of building materials and the shading effect of nearby buildings and trees.
The maximum air temperature differences between the hottest and coldest sites reached 6.5 °C at day and 3.2 °C at night at the same time in different urban contexts. Air temperature differences were greater, especially during clear and calm weather conditions. This is largely attributable to the difference in radiative cooling rates between natural vegetation and building areas. Mature trees in the form of roadside plantings and plantings between buildings appeared able to provide good shading during the day, but did not provide any noticeable evaporation cooling at night. The long-wave heat release from the surrounding buildings and surfaces was much greater. Thus, areas with similar configuration would also show a relatively cool daytime air temperature and a much warmer nighttime air temperature.
At night, vegetated areas (Points (3), (19), and (20)) were more exposed to the sky than building areas and thus experienced a higher cooling rate. At the same time, the decrease in temperature in the building area was lower because surrounding structures influenced the loss of long-wave radiation to the sky.
To explore the driving mechanisms of air temperature differences varied with times, we analyzed the correlation between daytime air temperature and the nighttime air temperature (Figure 10). The significant correlation between the air temperature in the night time and that in the day time implies that the urban morphology parameters affecting the temperature are the same for the night time and day time. On the contrary, weak correlation indicates that the distinct parameters mainly dominate the temperature in the day time or night time . It can be seen in Figure 10 that the correlation between the temperature in the night time and that in the day time is rather weak (R2 = 0.24, p = 0.009), which indicates there exist other parameters affecting the temperature. During the day, the air temperature variations at different locations were influenced by more factors, such as the heat from window air conditioners and traffic. At nighttime, however, the spatial temperature pattern was more complex; air temperature differences may be mainly attributable to the differences in cooling, specifically, among different sites.
The cooling effect of vegetation was stronger at night than during the day per our standardized coefficients, although said effects varied slightly with calculation radius. This is mainly because vegetation inherently affects air temperature in different ways at different times. During the day, vegetation strongly impacts cooling temperature through partitioning solar radiation into latent heat rather than sensible heat. At daytime, shading from vegetation also produces cooling effect on ambient air temperature. During nighttime, however, the lower air temperature in vegetated areas is mainly due to the elevated radiative cooling rate. Thus, it seems that the cooling effect of vegetation produced by a higher cooling rate in the vegetated area at night could exceed that produced by a combination of evapotranspiration and shading during the day. We also found that an increase in BPR also significantly decreased air temperature during the daytime but increased it during the nighttime. The impact of BPR is in providing shading during the day and dissipating heat as radiative energy, resulting in a lower daytime temperature and higher nighttime temperature. In a tropical climate, high BPR can reduce the speed of winds which would otherwise carry heat away from buildings. Previous studies have indicated that the intra-urban air temperature is also related to urban geometry as-measured by H/W (height/width) ratio or SVF . Suitable shading and sufficiently wide wind corridors can both be controlled appropriately by adjusting the H/W ratio.
Air temperature in our study area increased with increasing distance from the nearest park or water body, and more clearly in nighttime than in daytime (Figure 9a,c). In Singapore, Chen and Wong  carried out measurements in two large parks to also find that air temperature gradually increases with increasing distance from the park boundary. These results may be indicative of an extension of the park’s cooling effect into its surroundings, suggesting that parks modify the urban thermal environment. The relationship between air temperature and distance to water (R2 = 0.32, p = 0.009) was very similar to the relationship between air temperature and distance to park (R2 = 0.28, p = 0.002). A combination of two factors likely explains this relationship. First, a water body is moist and cool compared to its surroundings and therefore may impact the microclimate of the neighborhood; parks function similarly. Second, in our study area, there is a water body located in the center of the park so there was a complex cooling effect exerted by both elements.
In summary, we have affirmed the comprehensive affecting radius of vital urban morphology parameters, including SVF, BPR, GnPR, PP, DP and DW, on the air temperatures has been affirmed to be 50m during the whole day period in Singapore for the first time. In addition, the most important parameter to affect the daytime air temperature is BPR and SVF. In the nighttime, GnPR was the only significant predictor of air temperature. This work has illustrated the systematic research paradigm to study the urban microclimate. Noteworthy, this work would also offer meaningful value of reference for urban planners and landscape designers to effectively alleviate the hot island effect in tropical cities such as Singapore.
The material of study is based on collaborative research project of Development of a Climate Change Information Service (CLICIS)@GeoSpace. The authors wish to thank members of the National Environment Agency for the support of this work. Any opinions, findings, and conclusions or recommendations expressed in this study are those of authors and do not necessarily reflect those of the National Environment Agency.
P.C., N.H.W. and H.J. conceived and designed the experiments; P.C. performed the experiments; P.C. analyzed the data; N.W. and M.I. contributed reagents/materials/analysis tools; P.C. wrote the paper.
Conflicts of Interest
The authors declare no conflict of interest.
- Oke, T.R. The energetic basis of the urban heat island. Q. J. R. Meteorol. Soc. 1982, 108, 1–24. [Google Scholar] [CrossRef]
- Alavipanah, S.; Wegmann, M.; Qureshi, S.; Weng, Q.; Koellner, T. The role of vegetation in mitigating urban land surface temperatures: A case study of Munich, Germany during the warm season. Sustainability 2015, 7, 4689–4706. [Google Scholar] [CrossRef]
- Santamouris, M. Heat island research in Europe: The state of the art. Adv. Build. Energy Res. 2007, 1, 123–150. [Google Scholar] [CrossRef]
- Jeong, S.Y.; Yoon, S.H. Method to quantify the effect of apartment housing design parameters on outdoor thermal comfort in summer. Build. Environ. 2012, 53, 150–158. [Google Scholar] [CrossRef]
- Eliasson, I. The use of climate knowledge in urban planning. Landsc. Urban Plan. 2000, 48, 31–44. [Google Scholar] [CrossRef]
- Brown, R.D. Ameliorating the effects of climate change: Modifying microclimates through design. Landsc. Urban Plan. 2011, 100, 372–374. [Google Scholar] [CrossRef]
- Jusuf, S.K.; Wong, N.H.; Wong, Z.Y.; Tan, E. Transformation of industrial planning in Singapore: Study on the micro-climatic condition of different industrial estates. Build. Environ. 2014, 80, 48–60. [Google Scholar] [CrossRef]
- Givoni, B. Impact of planted areas on urban environmental quality: A review. Atmos. Environ. Part B Urban Atmos. 1991, 25, 289–299. [Google Scholar] [CrossRef]
- Salata, F.; Golasi, I.; Petitti, D.; de Lieto Vollaro, E.; Coppi, M.; de Lieto Vollaro, A. Relating microclimate, human thermal comfort and health during heat waves: An analysis of heat island mitigation strategies through a case study in an urban outdoor environment. Sustain. Cities Soc. 2017, 30, 79–96. [Google Scholar] [CrossRef]
- Lee, H.; Mayer, H.; Chen, L. Contribution of trees and grasslands to the mitigation of human heat stress in a residential district of Freiburg, Southwest Germany. Landsc. Urban Plan. 2016, 148, 37–50. [Google Scholar] [CrossRef]
- Yu, C.; Hien, W.N. Thermal benefits of city parks. Energy Build. 2006, 38, 105–120. [Google Scholar] [CrossRef]
- Skelhorn, C.; Lindley, S.; Levermore, G. The impact of vegetation types on air and surface temperatures in a temperate city: A fine scale assessment in Manchester, UK. Landsc. Urban Plan. 2014, 121, 129–140. [Google Scholar] [CrossRef]
- Upmanis, H.; Chen, D. Influence of geographical factors and meteorological variables on nocturnal urban park temperature differences a case study of summer 1995 in Göteborg, Sweden. Clim. Res. 1999, 13, 125–139. [Google Scholar] [CrossRef]
- Ca, V.T.; Asaeda, T.; Abu, E.M. Reductions in air conditioning energy caused by a nearby park. Energy Build. 1998, 29, 83–92. [Google Scholar] [CrossRef]
- Oke, T.R.; Johnson, G.T.; Steyn, D.G.; Watson, I.D. Simulation of surface urban heat islands under ‘ideal’ conditions at night Part 2: Diagnosis of causation. Bound. Layer Meteorol. 1991, 56, 339–358. [Google Scholar] [CrossRef]
- Sun, C.Y. A street thermal environment study in summer by the mobile transect technique. Theor. Appl. Climatol. 2011, 106, 433–442. [Google Scholar] [CrossRef]
- Yan, H.; Fan, S.; Guo, C.; Wu, F.; Zhang, N.; Dong, L. Assessing the effects of landscape design parameters on intra-urban air temperature variability: The case of Beijing, China. Build. Environ. 2014, 76, 44–53. [Google Scholar] [CrossRef]
- Yokobori, T.; Ohta, S. Effect of land cover on air temperatures involved in the development of an intra-urban heat island. Clim. Res. 2009, 39, 61–73. [Google Scholar] [CrossRef]
- Eliasson, I. Urban nocturnal temperatures, street geometry and land use. Atmos. Environ. 1996, 30, 379–392. [Google Scholar] [CrossRef]
- Liang, J.; Gong, J.; Sun, J.; Liu, J. A customizable framework for computing sky view factor from large-scale 3D city models. Energy Build. 2017, 149, 38–44. [Google Scholar] [CrossRef]
- Golasi, I.; Salata, F.; de Lieto Vollaro, E.; Coppi, M.; de Lieto Vollaro, A. Thermal perception in the mediterranean area: Comparing the mediterranean outdoor comfort index (moci) to other outdoor thermal comfort indices. Energies 2016, 9, 550. [Google Scholar] [CrossRef]
- Krüger, E.; Rossi, F.; Drach, P. Calibration of the physiological equivalent temperature index for three different climatic regions. Int. J. Biometeorol. 2017, 61, 1323–1336. [Google Scholar] [CrossRef] [PubMed]
- WEATHER Wise Singapore. National Environment Agency. Available online: http://app2.nea.govsg/data/cmsresource/20090721544571208250.pdf (accessed on 21 July 2009).
- Wong, N.H.; Yu, C. Study of green areas and urban heat island in a tropical city. Habitat Int. 2005, 29, 547–558. [Google Scholar] [CrossRef]
- Bahi, H.; Rhinane, H.; Bensalmia, A.; Scherer, D. Effects of urbanization and seasonal cycle on the surface urban heat island patterns in the coastal growing cities: A case study of Casablanca, Morocco. Remote Sens. 2016, 8, 829. [Google Scholar] [CrossRef]
- Geletič, J.; Lehnert, M.; Dobrovolný, P. Land Surface Temperature Differences within Local Climate Zones, Based on Two Central European Cities. Remote Sens. 2016, 8, 788. [Google Scholar] [CrossRef]
- Wang, J.; Zhan, Q.; Guo, H. The Morphology, Dynamics and Potential Hotspots of Land Surface Temperature at a Local Scale in Urban Areas. Remote Sens. 2015, 8, 18. [Google Scholar] [CrossRef]
- Sismanidis, P.; Keramitsoglou, I.; Kiranoudis, C.T.; Bechtel, B. Assessing the capability of a downscaled urban land surface temperature time series to reproduce the spatiotemporal features of the original data. Remote Sens. 2016, 8, 274. [Google Scholar] [CrossRef]
- Jusuf, S.K. Development of Estate Level Climate Related Impact Assessment Framework and Air Temperature Prediction within Urban Climatic Mapping Method in Singapore. Ph.D. Thesis, National University of Singapore, Singapore, 2009. [Google Scholar]
- Matzarakis, A.; Rutz, F.; Mayer, H. Modelling radiation fluxes in simple and complex environments—Application of the RayMan model. Int. J. Biometeorol. 2007, 51, 323–334. [Google Scholar] [CrossRef] [PubMed]
- Wong, N.H.; Jusuf, S.K.; Tan, C.L. Integrated urban microclimate assessment method as a sustainable urban development and urban design tool. Landsc. Urban Plan. 2011, 100, 386–389. [Google Scholar] [CrossRef]
- American Society of Heating, Refrigerating and Air Conditioning Engineers (ASHRAE). Handbook A, Fundamentals; American Society of Heating, Refrigerating and Air Conditioning Engineers: Atlanta, GA, USA, 2001; pp. 99–110. ISBN 0910110565. [Google Scholar]
- International Standard Organization (ISO). ISO 7726, Ergonomics of the Thermal Environment, Instruments for Measuring Physical Quantities; International Standard Organization: Geneva, Switzerland, 1998; pp. 45–51. ISBN 058038651. [Google Scholar]
- Ong, B.L. Green plot ratio: An ecological measure for architecture and urban planning. Landsc. Urban Plan. 2003, 63, 197–211. [Google Scholar] [CrossRef]
- Zakşek, K.; Bechtel, B. Source area estimation of urban air temperatures. Urban Remote Sens. Event (JURSE) 2015, 1–4. [Google Scholar] [CrossRef]
- Krüger, E.; Givoni, B. Outdoor measurements and temperature comparisons of seven monitoring stations: Preliminary studies in Curitiba, Brazil. Build. Environ. 2007, 42, 1685–1698. [Google Scholar] [CrossRef]
- Bernard, J.; Musy, M.; Calmet, I.; Bocher, E.; Keravec, P. Urban heat island temporal and spatial variations: Empirical modeling from geographical and meteorological data. Build. Environ. 2017, 125, 423–438. [Google Scholar] [CrossRef]
- Hien, W.N.; Jusuf, S.K. Air temperature distribution and the influence of sky view factor in a green Singapore estate. J. Urban Plan. Dev. 2009, 136, 261–272. [Google Scholar] [CrossRef]
- Chow, W.T.L.; Roth, M. Temporal dynamics of the urban heat island of Singapore. Int. J. Climatol. 2006, 26, 2243–2260. [Google Scholar] [CrossRef]
- Johansson, E. Influence of urban geometry on outdoor thermal comfort in a hot dry climate: A study in Fez, Morocco. Build. Environ. 2006, 41, 1326–1338. [Google Scholar] [CrossRef]
Figure 1. Location of the study area and measurement sites.
Figure 2. Map view of fixed test points.
Figure 3. Weather station structure.
Figure 4. Time deviations between predicted and detected temperatures.
Figure 5. Profiles of (a) air temperature and (b) RH from 0:00 UTC to 24:00 UTC for all testing points.
Figure 6. Mapping of the microclimate parameters.
Figure 7. Relationships between microclimate parameters and SVF during day and night with the radius of 50 m.
Figure 8. Relationships between microclimate parameters with BPR and GnPR during day and night with the radius of 50 m.
Figure 9. Relationships between microclimate parameters and spatial parameters during day and night with the radius of 50 m.
Figure 10. Relationships between daytime temperature and nighttime temperature.
Table 1. The mean annual trends of air temperature, relative humidity and wind speed.
|Time Period||Average Temperature (°C)||Average Number of Rainy Days||Average Morning Relative Humidity (%)||Average Evening Relative Humidity (%)||Average Wind Speed (km/h)|
Table 2. Technical characteristics of measurement instruments.
|Global temperature (Tg)||−40 °C to 70 °C, ± 0.18 °C|
|ONSET HOBO U23-001|
|Temperature range/accuracy||−40 °C to 70 °C, ±0.2 °C|
|RH measurement range/accuracy||0–100%, ±2.5%|
|Wind speed/direction||ONSET S-WSET-A Wind speed & direction sensor|
|Wind direction range||2-Axis ultrasonic wind sensor|
|Wind speed range/accuracy||0–45 m/s (0–100 mph) ±1.1 m/s (2.4 mph)|
|Data logger||HOBO Micro station logger H21-002||−25 °C to 65 °C|
|Sky view factor (SVF)||Nikon D80 Digital SLR camera with fish eye lens|
Table 3. Selected date for model development and validation.
|40 Days for Model Development||10 Days for Model Validation|
|February 2017||2, 8, 9, 25||February 2017||3, 10,26|
|March 2017||5, 7, 8, 16||April 2017||6, 10, 15|
|April 2017||2, 5, 6, 10, 13||July 2017||4, 15|
|May 2017||25, 26, 27||August 2017||18, 21|
|June 2017||6, 8, 11, 13, 15, 25, 27||September 2017||18, 20|
|July 2017||1, 3, 5, 6, 10, 18, 21|
|August 2017||17, 22, 23, 25, 26, 27|
|September 2017||5, 7, 8, 16|
|October 2017||1, 6, 10, 18|
Table 4. Description of measuring sites (50 m).
|No||SVF||BPR||GnPR||PP (%)||DP (m)||DW (m)||Temp. (°C)||RH (%)||Tmrt (°C)||Description of Measurement Sites|
|1||0.76||1||1.06||70||506||188||30.77||72.88||31.71||Broad street, multi-story buildings|
|2||0.57||0.35||1.06||63.6||757||397||29.76||77.24||30.32||Broad street, multi-story buildings|
|3||0.38||0||1.25||8.5||238||150||29.16||79.76||29.75||Park’s perimeter road, tree cover|
|4||0.62||1.86||0.20||51.2||769||458||30.01||75.01||30.52||High-rise buildings without trees|
|5||0.48||5.72||3.24||50||919||606||29.59||79.09||29.77||Broad street, high-rise buildings|
|6||0.51||2.28||0.62||47.2||714||1028||30.04||77.18||30.06||Broad street, open space|
|7||0.32||4.3||0.41||31.2||1256||1112||28.94||81.45||29.28||High-rise buildings, tree cover|
|8||0.51||0.08||0.43||30.4||767||958||29.79||78.75||30.25||High-rise buildings, tree cover|
|9||0.34||5.7||1.64||28.1||1124||1195||29.09||81.17||29.68||Broad street, multi-story buildings|
|10||0.52||3.2||2.95||51.4||1229||1410||29.51||80.24||30.2||Broad street, multi-story buildings|
|11||0.46||2.4||1.0||19.7||1453||1539||29.19||84.56||30.4||Open area with lawn|
|12||0.32||3.7||1.55||9.6||1521||1778||29.43||79.76||31.44||Broad street, multi-story buildings|
|13||0.68||0.8||1.89||63.1||1455||1751||30.01||73.46||31.41||Shopping mall without tree|
|14||0.55||1.05||0.16||31.7||1020||1325||30.21||76.50||30.02||Multi-story buildings, tree cover|
|15||0.48||2.42||0.41||50.8||937||1254||29.24||80.41||30.01||Multi-story buildings, tree cover|
|16||0.61||1.9||2.59||31.8||695||994||29.41||81.26||30.03||Open area with few tree|
|17||0.51||1.8||3.85||21.3||505||791||29.43||75.11||30.01||Multi-story buildings, tree cover|
|18||0.37||5.4||3.43||29.4||224||520||28.99||83.51||29.38||Broad street, multi-story buildings|
|19||0.66||0.1||0.49||34.2||122||150||30.39||78.90||30.11||Open area with lawn|
|20||0.82||0||0.17||33||185||10||30.87||75.03||31.12||Inside the park, open area with lawn|
|21||0.41||0.37||3.0||47.4||148||514||29.64||77.13||30.25||Open area, parking lot|
|22||0.44||0.22||0.58||30.8||289||443||29.51||76.96||30.44||Open area, parking lot, tree cover|
|23||0.54||1.05||1.97||20.7||569||882||29.69||75.57||30.45||High-rise buildings, tree cover|
|24||0.72||1.17||2.78||61.9||579||883||29.89||78.21||31||Open area without tree|
|25||0.59||1.57||0.69||30.1||630||980||29.89||78.21||30.95||Multi-story buildings without tree|
|26||0.51||0.9||1.29||40.8||1011||1406||29.81||75.33||30.1||Open area with tree|
|27||0.33||0.9||4.37||42.9||1351||1774||29.59||74.87||29.67||Open area with tree|
Abbreviations: SVF, sky view factor; BPR, building plot ratio; GnPR, green plot ratio; PP, percentage of pavement; DP, distance to park; DW, distance to water body.
Table 5. Regression results of air temperature and six landscape variables. The bold figures are significant variable with p < 0.05.
|Variables||20 m||50 m||70 m|
Abbreviations: B, unstandardized coefficient; Beta, standardized coefficient; and Sig., significant level. Note: This research set 0.05 as the threshold and significance indicates that, when p value < 0.05, the variables can effectively explain the change of temperature. Note: the figures in bold are significant variable with p < 0.05.
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