1. Introduction
Infiltration and exfiltration, driven by pressure differences across a building envelope, cause uncontrolled heating and cooling loads, leading to energy loss [
1]. In multi-family residential high-rise buildings (MFRHBs), infiltration accounts for a significant portion of winter energy consumption [
2,
3] underscoring the importance of accurately assessing the building energy performance. Moreover, inaccurate estimation of the infiltration rate can lead to significant errors in both predicting energy consumption and appropriately sizing HVAC systems [
4,
5]. Ng et al. [
6] reported that improving infiltration settings in EnergyPlus increased HVAC electricity use by 3% and heating gas consumption by 8%. Heibati et al. [
7] likewise showed that different airtightness assumptions for the same building lead to significant variations in calculated heating and cooling design loads. These findings further indicate that infiltration and leakage across the building envelope present the significant influence on building energy performance and HVAC system operations. Furthermore, the NREL Strategy Guideline further noted that the combined adjustments to design conditions, envelope characteristics, duct characteristics, and ventilation–infiltration parameters can overestimate cooling loads by up to 161%, consequently resulting in oversized equipment, increased costs, and reduced part-load efficiency [
8]. Therefore, it is essential to accurately estimate infiltration rates for code compliance and reliable HVAC design.
Since the infiltration rate is driven by the pressure difference (
) across the building envelope, its calculation requires a prior assessment of the envelope pressure distribution [
9]. Airtightness performance indicators related to infiltration are commonly expressed as Cubic Meter per Hour at 50 Pa (CMH
50), Air Change rate per Hour at 50 Pa (ACH
50), and Effective Leakage Area (ELA), which are measured using pressurized or depressurized tests at a reference
between the indoors and outdoors [
10]. However, the actual indoor–outdoor
is generally less than 10 Pa for low-rise detached houses [
11,
12], while it ranges from approximately 25 Pa to 30 Pa for high-rise buildings and depends on the building height [
13]. Because the actual pressure difference acting on the envelope significantly differs from the 50 Pa reference pressure used in the pressurization-depressurization method, it is necessary to convert the measured flow rate at 50 Pa (
) to estimate the natural infiltration rate (
).The conversion coefficient (
) is primarily used for this conversion and is defined as a dimensionless parameter representing the ratio between
and
. Currently,
is widely recommended, mainly based on studies for low-rise buildings [
14]. However, the natural infiltration rate varies with environmental parameters such as building characteristics, wind conditions, and indoor-outdoor temperature differences. Consequently, the uniform application of a single constant
can introduce considerable errors into the analysis results. The validity and uncertainty associated with this coefficient have been subjects of continuous research [
15,
16,
17,
18,
19,
20]. For example, Turner et al. [
20] evaluated the variability of
under different meteorological conditions using an infiltration model; however, the study was limited to low-rise buildings and thus did not adequately account for the height-dependent
characteristic of high-rise buildings. Unlike low-rise buildings, high-rise buildings exhibit a distinct vertical pressure gradient with height, which must be reflected in the analysis [
21].
Simulation tools such as EnergyPlus and TRNSYS currently estimate infiltration rates using the single-zone method based on the Effective Leakage Area (ELA) concept [
22]. However, this approach cannot accurately represent the floor-by-floor
in high-rise buildings, as it does not sufficiently account for variations in height. Although commercial simulation programs and multi-zone network models can analyze infiltration, their practical application is often limited by the extensive input data required and the computational complexity involved [
23]. Therefore, evaluating infiltration in high-rise buildings requires a simplified approach that incorporates the coefficient
. This process involves calculating the average natural infiltration rate, which is obtained by normalizing existing data to determine representative
value.
This study extends the conventional LBL model that is mainly applied for single-zone and low-rise buildings, which help evaluate natural infiltration in high-rise buildings. A calculation process is proposed to determine representative N values that reflect pressure variations associated with building height and seasonal meteorological conditions. This approach addresses the inherent limitations of the traditional single-zone model, providing a simplified and reliable framework for evaluating natural infiltration in high-rise buildings.
3. Methodology for the Conversion Coefficient
The calculation of the conversion coefficient proposed in this study is based on the application of the existing ELA model, treating each floor as an independent single zone. In multi-unit high-rise residential buildings, each unit is inherently separated by a floor slabs, which allows each floor to be reasonably regarded as an individual zone. Consequently, this approach enables an analysis that incorporates the height-dependent pressure differences, which were not adequately reflected in the conventional ELA model.
Figure 1 illustrates this conceptual distinction by comparing the traditional single-zone assumption with the proposed multi-floor framework. The figure highlights how the pressure distribution along the building height, including the neutral pressure level (NPL) and its vertical gradient, leads to different infiltration patterns at each floor.
It should be noted that the proposed model in this study is developed based on several fundamental assumptions to enhance simplification and computational efficiency. The geometric configuration of the target building is idealized as a two-dimensional (2D) rectangular domain, while air leakage paths through the envelope are represented using the equivalent orifice flow equation under the assumption of fully turbulent flow conditions. In addition, a single-zone modeling approach is applied to each floor, whereby the pressure difference is assumed to be uniformly distributed across the building envelope. The indoor–outdoor air density difference is also considered constant, implying that the stack-effect-induced pressure varies linearly with height.
Figure 2 illustrates the process of deriving the final
using the measured
and
. The procedure is further structured into five main steps: (1) Meteorological Data Processing and Normalization, (2) Selection of Representative Pressure Difference, (3) Preprocessing of Measured Airtightness Data, (4) Calculation of Natural Infiltration Rate, and (5) Derivation of Final Conversion Coefficient. The detailed explanations of each step are shown below.
Step 1. Meteorological Data Processing and Normalization
To ensure the objectivity of the calculated natural infiltration rate, the meteorological data (outdoor temperature and wind speed) used in the analysis undergoes statistical verification through the Jarque–Bera Test. This test assesses the normality of the dataset, which determines whether the mean or median should be used as the representative value in subsequent calculations. The statistically verified meteorological data are then used as input for calculating the floor-by-floor pressure difference. The Jarque–Bera Test evaluates whether a dataset follows a normal distribution based on its skewness (
) and kurtosis (
). When the meteorological data exhibit non-normality, the median is adopted instead of the mean, ensuring the robustness of the analysis. The Jarque–Bera Test statistic (
) is calculated as follows [
30].
where
is the number of data points. A smaller
value indicates that the dataset is closer to a normal distribution, providing the criterion for selecting representative meteorological data. If the
p-value of the test is less than the significance level, indicating non-normality, the median is used; otherwise, the mean is applied.
Before being used in the pressure calculation to derive
, the collected meteorological data are aggregated at hourly, daily, and monthly intervals. Therefore, it is necessary to identify an appropriate representative time scale by comparing the error rates among different aggregation periods. This step aims to prevent
from being biased toward a specific time interval and to ensure that it represents a stable long-term average. The calculation result from the smallest time unit (i.e., the dataset containing the highest number of observations) is set as the reference, and the error rate is compared with that of the next larger time unit to balance simplicity and accuracy. If the error rate is less than 5%, this indicates that the increase in the data measurement interval introduces only a minor error. In this case, the reference unit is updated to the next larger time interval, which contains fewer data points but represents a broader timescale. Conversely, if the error rate is 5% or greater, the error resulting from data reduction is considered significant, and the previous time interval is finalized as the representative unit. This iterative process continues until the optimal time interval for
calculation is conclusively determined. The selection logic can be summarized as follows:
where
denotes the statistically determined representative value (mean or median) of the meteorological variable (e.g., outdoor temperature or wind speed) for each interval, as determined from the normality assessment.
Step 2. Selection of Representative Pressure Difference
The meteorological data derived are used to calculate the pressure difference caused by the stack effect () and the wind pressure (). For evaluating the natural infiltration rate, only the magnitude of the pressure difference is considered.
The
varies linearly with building height relative to the NPL and is proportional to the height difference between the NPL and the target floor. For application in the ELA model, the
on each floor is assumed to act as an average pressure difference applied at the floor’s center (
). However, for the floor where the NPL is located, the
acts in opposite directions simultaneously—negative (−) above and positive (+) below the NPL—centered at the NPL [
21]. As illustrated in
Figure 3, the representative pressure difference (
) for this floor is calculated as the weighted average of the magnitudes of the pressure differences, with each direction weighted according to its relative influence.
The
for a typical floor that does not contain the NPL (denoted as
) is calculated using Equation (9), while that for the floor containing the NPL is determined using Equation (10):
where
is the height of the floor center, obtained by subtracting half of the floor height (
) from the height from the ground to the ceiling of that floor (
).
denotes the height of the NPL.
and
represent the outdoor and indoor temperatures, respectively, and
is obtained from meteorological data. Specifically, for the calculation of
on the NPL floor—where the geometric mean of the pressure distribution is required—
(the vertical distance from the floor bottom to the NPL) and
(the distance from the NPL to the ceiling) are used.
and
represent the average pressure magnitudes in the lower and upper portions of the NPL floor, respectively. These values are then combined using a weighted average to determine the representative pressure for the NPL floor. The floor-by-floor wind pressure is determined by the wind speed at the corresponding height. Because its variation with height exhibits non-linear characteristics, the median is adopted as the representative value. This approach provides greater robustness than the mean, as wind-induced pressure variations can fluctuate sharply with height or be influenced by localized flow conditions. The wind pressure is calculated as follows:
where
denotes the wind speed obtained from the meteorological agency. Because wind speed varies with the measurement environment, it must be adjusted to reflect the conditions at the building site. Therefore, to calculate the wind pressure acting on the building envelope, the boundary layer thickness (
) and the wind speed exponent (
) specified in ASHRAE are applied [
31]. This process converts the reference wind speed from the meteorological agency into the actual wind speed at each corresponding floor height, which is then used to calculate the final wind pressure.
In energy simulation programs, a building’s infiltration rate is often represented as a single overall value by modeling the entire building as one zone, rather than modeling each dwelling unit separately [
22]. Therefore, to derive a single representative
N for the entire building, the pressure difference due to the stack effect (
) and wind pressure (
) were calculated using a model that treats the whole building as a single zone. The overall stack effect pressure distribution for the building is analogous to that of the NPL floor, as the NPL is typically located near the middle of the building height. Accordingly,
is calculated, similar to Equation (10), by averaging the pressures in the upper and lower sections and then applying height-based weighting to determine the geometric mean. Similarly,
is obtained by substituting the height variable
in Equation (11) with the building’s mid-height,
.
Step 3. Preprocessing Measured Airtightness Data
The final equation for
depends on the pressure exponent obtained from the measured data. Data acquired through the pressurization-depressurization test at 50 Pa often contains outliers caused by temporary pressure fluctuations or measurement errors [
32]. Therefore, an outlier remover process was applied to ensure the reliability and robustness of the derived building characteristic parameter. Since
is calculated as the ratio of
and
, the flow coefficient cancels out in the final
equation, making the accuracy of the pressure exponent critical. The Interquartile Range (IQR) method was employed for outlier detection [
33], where data points outside the quartile-based boundaries are outliers and excluded from the analysis.
Step 4. Calculation of Natural Infiltration Rate
The natural infiltration rate is calculated based on the ELA equation to determine the individual airflow rates driven by pressure differences (
). These two components are then combined into
using the root-sum-square method (Equation (3)). To account for the leakage characteristics of each floor, the individual flow rates are computed using the pressure differences calculated for each floor (
). The infiltration rates caused by the stack effect and wind are further adjusted using the stack parameter (
) and wind parameter (
) [
29]. These parameters are introduced as reduction coefficients to compensate for the limitations of the single-zone ELA model, reflecting the non-uniform distribution of leakage across the building envelope and the complexity of an internal flow network. The following Equations (12)–(15) define the relationships with the leakage distribution parameters (
) and the shielding coefficient (
) proposed by Lawrence Berkeley Laboratory. It should be noted that the
shown in Equation (15) represents the wind speed attenuation factor accounting for façade pressure effects, and the recommended moderate value of 0.25 is applied in this study [
26]. Additionally, the square-root terms in Equations (12) and (14) originate from the orifice-flow formulation, which assumes a pressure exponent
n of 0.5 under fully turbulent flow.
where
represents the building’s shielding coefficient proposed by Lawrence Berkeley Laboratory [
34]. The parameter R is defined as the ratio of the sum of the ceiling and floor leakage areas (
) to the total leakage area (
) of the indoor space. The parameter
is defined as the ratio of the difference between the ceiling and floor leakage area (
) to the total leakage area. Because determining the exact leakage area of each surface in an actual building is practically difficult, an average approximation value of
was applied to apartment buildings [
35,
36,
37]. The parameter
indicates the vertical asymmetry in leakage area caused by the stack effect. When
,
takes a value of
when the ceiling leakage area (
) is dominant, and
when the floor leakage area (
) is dominant. Assuming maximum vertical infiltration, a uniform value of
was applied to all floors except the NPL floor.
Step 5. Derivation of Final Conversion Coefficient
Finally,
, which reflects the floor-by-floor pressure difference variations, is derived as the ratio of the measured infiltration rate obtained from the pressurization–depressurization test to the natural infiltration rate calculated using the ELA model. The final equation is presented as Equation (16).
4. Application and Verification
To verify the practicality of the proposed methodology for calculating the conversion coefficient, the process was applied to a high-rise residential building in South Korea. The target building has 45 stories, with an average floor height of 3 m. Internal shaft temperatures and other necessary input data for pressure calculation were obtained from previous studies [
31,
38,
39].
Table 2 summarizes the parameters and detailed information used for the application of the proposed methodology.
The results from the Jarque–Bera Test indicated that the measured wind speed and temperature data did not follow a normal distribution. Consequently, the median, which is less sensitive to outliers, was adopted as the representative value. In the time-scale analysis, hourly data was used for outdoor temperature due to its pronounced diurnal variation, whereas daily data was used for wind speed, given its smaller range of variation and to improve computational efficiency. Typically, a pressure exponent of 0.6 is employed in building air infiltration analyses [
40]. This value was applied to calculate the natural infiltration rate and the conversion coefficient.
As shown in
Figure 4, the minimum value of
was observed near the NPL, which was assumed to be located at the building’s midpoint (23rd floor) in this study. This occurs due to the minimal indoor–outdoor pressure difference in this region. Conversely, the
values exhibited a substantial increase, showing an inverse relationship with
. The seasonal analysis indicated that the natural infiltration rate was generally higher in winter, when the driving force of the stack effect is stronger. The vertical variation of
ranged from a minimum of 6.5 to a maximum of 27.9 in summer, and from 4.5 to 23.4 in winter. Notably, in winter, the
value for the floors near the NPL and for the top/bottom floors differed by more than fivefold. This pronounced floor-by-floor variation clearly demonstrates that applying a single uniform
N to represent the entire building can lead to substantial errors for individual floors.
However, as noted in the previous sections, a building’s energy performance is often evaluated using a single representative value for the entire structure. Therefore, it is necessary to determine a building-average conversion coefficient (
) based on the representative pressure value calculated for the whole building.
Figure 5 presents the variation of
NAvg across different building heights, using meteorological data from South Korea and a pressure exponent of 0.6. In particular, low-rise, mid-rise, and high-rise buildings correspond to 4-story (12 m), 20-story (60 m), and 45-story (135 m) buildings, respectively. The results indicate that the average
for high-rise buildings was 8.8 in summer and 6.2 in winter. For mid-rise buildings, the values were 12.9 in summer and 9.3 in winter, while for low-rise buildings, they were 27.4 and 20.9, respectively. These results demonstrate that low-rise buildings exhibit
values more than three times higher than those of high-rise buildings, confirming that
varies significantly with the variation in building heights. Furthermore, the average
values in summer and winter differed by approximately 20% was observed across all building types.
The preceding analysis of floor-specific and seasonal values focused on confirming the overall trend of variability in the conversion coefficient assuming a common pressure exponent of 0.6. To verify the distribution of
under actual environmental conditions based on the proposed methodology, we analyzed airtightness data obtained from measurements conducted in South Korea. A total of 1175 individual dwelling units across 13 multi-family residential complexes were included in the analysis to derive an objective conversion coefficient representative of real conditions, and the summary of test samples is shown in
Table 3.
Prior to calculating the
values using the representative pressure difference, a data preprocessing procedure was conducted.
Figure 6 presents the box plots illustrating the distributions of the measured flow coefficient and the pressure exponent for all 1175 samples. As a result of the outlier removal process, a total of 1106 valid data points were selected from the 1175 initial measurement records. The final dataset exhibited a flow coefficient range of 31 to 167 (m
3/(s·Pa
n)) and a pressure exponent range of 0.54 to 0.69.
Figure 7 presents the conversion coefficient, derived from the measured airtightness data, as the Probability Density Function (PDF) for summer and winter conditions in Korea. The representative
value, obtained through weighted averaging of the measured data, clearly demonstrates a significant dependence on building height. For low-rise buildings,
ranged from 23 to 33 in summer, 21 to 30 in interseason, and 21 to 29 in winter. For mid-rise buildings, the ranges were from 10 to 16 in summer, 10 to 15 in interseason, and 8 to 12 in winter. High-rise buildings exhibited the lowest values, ranging from 7 to 11 in summer, 7 to 10 in interseason, and 5 to 8 in winter. As building height increased, not only did the overall
values decrease, but the seasonal variation and range of
also became narrower. Therefore, applying a conversion coefficient that appropriately reflects both climatic and height characteristics is essential for accurate energy performance evaluations. This finding supports the use of height-specific
values in building energy simulations.
In addition, it should be noted that the
values calculated for low-rise buildings were generally consistent with the previously published range of 20–30, as summarized in
Table 1. Furthermore, research reports published by NYSERDA and the U.S. Department of Energy [
41] indicated that the ratio of
/
for mid-rise residential buildings with 11–13 stories ranged from 7.9 to 9.25. This result aligns well with the
value range (8–15.5) derived for mid-rise buildings in this study. Although the
values for high-rise buildings are limited in the existing literature, the overall consistency between the derived
values and previously reported results for low- and mid-rise buildings supports the validity and reliability of the proposed model.