Journal Pre-proof Optimal design of classroom spaces in naturally-ventilated buildings to maximize occupant satisfaction with human bioeffluents/body odor levels Dario F. Acosta-Acosta, Khaled El-Rayes PII:
S0360-1323(19)30755-3
DOI:
https://doi.org/10.1016/j.buildenv.2019.106543
Reference:
BAE 106543
To appear in:
Building and Environment
Received Date: 28 June 2019 Revised Date:
25 October 2019
Accepted Date: 11 November 2019
Please cite this article as: Acosta-Acosta DF, El-Rayes K, Optimal design of classroom spaces in naturally-ventilated buildings to maximize occupant satisfaction with human bioeffluents/body odor levels, Building and Environment, https://doi.org/10.1016/j.buildenv.2019.106543. This is a PDF file of an article that has undergone enhancements after acceptance, such as the addition of a cover page and metadata, and formatting for readability, but it is not yet the definitive version of record. This version will undergo additional copyediting, typesetting and review before it is published in its final form, but we are providing this version to give early visibility of the article. Please note that, during the production process, errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain. © 2019 Elsevier Ltd. All rights reserved.
1 2 3
Optimal design of classroom spaces in naturally-ventilated buildings to maximize occupant satisfaction with human bioeffluents/body odor levels
4 5 6 7 8 9 10
Dario F Acosta-Acosta a,b,*, Khaled El-Rayes a
11
Abstract
a
Dept. of Civil and Environmental Engineering, Univ. of Illinois at Urbana-Champaign. Address: 3112 Newmark Civil Engineering Bldg, 205 N. Mathews, 61801, Urbana, Illinois, US. b Facultad de Ingeniería, Universidad Panamericana Campus Guadalajara. Present address: Álvaro del Portillo No. 49, Ciudad Granja, 45010, Zapopan, Jalisco, México.
12
Inadequate indoor air quality in education buildings has been reported to cause health
13
problems, contagion, poor academic performance and absenteeism of occupants. To minimize
14
these adverse effects, the use of natural ventilation systems and hybrid ventilation systems in
15
buildings have increased in recent years. This paper presents the development of a novel
16
optimization model that provides the capability of optimizing education building design in order
17
to maximize occupant satisfaction in the classrooms space in terms of perception of human
18
bioeffluents/body odor while minimizing the construction cost. The multi-objective optimization
19
model is developed in three main stages: (1) model formulation stage that identifies relevant
20
design variables, objective functions and constraints; (2) model implementation stage that
21
executes the optimization computations; and (3) model evaluation stage that analyses the
22
performance of the developed model using an application example. The findings of this
23
performance analysis illustrates the capability of the developed optimization model to generate a
24
wide range of optimal trade-offs solutions, where each provides a unique and optimal trade-off
25
between occupant satisfaction with human bioeffluents/body odor levels and its construction
26
cost. This enables designers to generate and analyze these optimal trade-offs and accordingly *
Corresponding author. Tel.: +52 (33) 1368 2200, fax: +52 (33) 2306 4093. e-mail:
[email protected].
27
identify an optimal set of design decisions that maximize satisfaction with human
28
bioeffluents/body odor levels of occupants while complying with specified budget constraint.
29
Keywords: Natural ventilation; Indoor air quality; Human Bioeffluents; Human Body
30
Odor; Education buildings; Multi-objective genetic algorithm.
31
1. Introduction
32
Education buildings are used on a daily basis by 29% of the US population that include
33
58.0 million students in schools, 19.2 million students in colleges and universities, and 10.9
34
million faculty and staff who spend a major part of their daytime in these buildings [1–3]. The
35
total floor space of education buildings was reported to be 12,237 million square feet, which
36
represents approximately 14% of the total floor space of non-residential buildings in the US [2].
37
They are the second major consumer of energy in the category of commercial buildings with an
38
annual consumption of 820 trillion BTU [4]. The majority of education buildings are aging and
39
are reported to suffer from poor ventilation and antiquated HVAC systems [5]. This causes poor
40
indoor air quality (IAQ) in education buildings that has been linked to health problems,
41
contagion, poor academic performance and absenteeism of occupants [6–14].
42
The aforementioned poor indoor air quality in education buildings can be addressed by
43
improving natural and mechanical ventilation to supply fresh outside air into classrooms to dilute
44
and remove carbon dioxide (CO2) concentration and other airborne contaminants. CO2
45
concentration levels are used to evaluate indoor air quality in terms of human bioeffluents
46
acceptability and therefore, the adequacy of the ventilation rate to control body odor [15,16]. The
47
relationship between CO2 concentrations and the acceptability of a space in terms of human
48
bioeffluents/body odor has been experimentally-determined in both chambers and real buildings
49
[15]. Accordingly, ASTM standard D6245 and ASHRAE standard 62.1 recommends that the
50
difference between CO2 concentration of indoor and outdoor air be equal to or below 650 ppm
51
[15] or 700 ppm [17] to control human body odor at an acceptable level. The ASTM standard
52
states that this 650 ppm concentration difference, combined with an assumed outdoor CO2
53
concentration of 350 ppm, is the basis of the commonly-referenced guideline value for CO2 of
54
1000 ppm to control human body odor [15].
55
The use of natural ventilation systems (NVS) and hybrid ventilation systems (HVS) in
56
buildings have increased in recent years to improve their CO2 concentration and energy
57
consumption [18]. The use of these NVS and HVS to replace HVAC systems can lead to
58
significant savings in the energy consumption of education buildings [18–20] because HVAC
59
systems account for 55% of their total energy consumption [2]. A number of research studies
60
have been conducted to investigate and improve the use of NVS and HVS in buildings. These
61
studies focused on (1) analyzing and modeling the natural ventilation processes; (2) determining
62
the effectiveness of NVS and HVS in buildings; (3) improving the design of NVS and HVS in
63
buildings, and (4) optimizing the performance of natural and hybrid ventilated buildings.
64
First, several research studies were conducted to analyze and model natural ventilation
65
processes in buildings. For example, Swami and Chandra [21] analyzed wind pressure
66
coefficients that can be used to calculate natural ventilation airflow rates in buildings. Similarly,
67
Cóstola et al.
68
coefficients calculation on NV airflow rates. Other studies analyzed the performance of various
69
models and simulation tools that were developed to simulate natural and hybrid ventilated
70
buildings. For example, Gandhi et al. [25,26] analyzed how the available simulation tools and
71
methods are being used by practitioners and researchers for simulating mixed mode and
[22,23] and Muehleisen and Patrizi [24] analyzed the impact of pressure
72
naturally-ventilated buildings. Other studies utilized building energy simulation programs such
73
as EnergyPlus to model natural ventilation processes in buildings. For example, Zhai et al. [27]
74
assessed the accuracy of EnergyPlus in modeling thermal-induced airflows in naturally-
75
ventilated buildings by comparing its simulated results to field measurements obtained from
76
three existing buildings. Dols et al. [27,28] combined thermal, airflow and contaminant modeling
77
of naturally-ventilated buildings by coupling EnergyPlus with CONTAM, which is a multizone
78
building airflow and contaminant transport simulation tool. Other studies investigated the design
79
and performance of natural ventilation in atrium buildings [29–33]
80
Second, several studies focused on determining the effectiveness of NVS and HVS in
81
buildings in different climates. For example, Axley [34] developed a model to evaluate the
82
climate suitability of natural/hybrid ventilation to provide passive cooling in commercial
83
buildings in North America. Hiyama and Glicksman [35] proposed the use of target air change
84
rate as a new criterion to evaluate the potential energy savings of NVS during the early stages of
85
building design. Chen et al. [36] estimated the energy saving potential of NVS in 1854
86
geographical locations around the world based on their NV hours which represents the number of
87
hours in a year when the weather and indoor conditions are appropriate for natural ventilation.
88
That study reported that (a) subtropical high-land and Mediterranean climates in regions such as
89
California are more suitable for utilizing NVS, and (b) NV hours in several US locations ranged
90
from 2,248 hours in Houston to 7,197 hours in Los Angeles out of the total annual hours of
91
8,760.
92
Third, a number of studies were conducted to improve the design of NVS and HVS in
93
buildings. For example, Heiselberg [37] developed a natural ventilation design process that
94
integrates the design of heating, cooling, lighting, and ventilation of buildings. CIBSE [38]
95
provided guidelines for the design of NVS for non-residential buildings and for their selection,
96
specification, and integration of various types of ventilation components. Omrani et al. [39]
97
developed a process model to integrate and evaluate the natural ventilation design into the
98
overall building design process for multi-story buildings. Aflaki et al. [40] provided a number of
99
design recommendations to improve the performance of NVS in tropical climates, including (1)
100
providing shading at top of east and west openings, (2) setting the orientation of the building in
101
the direction of the dominant angles of wind and sun, (3) reducing the size of apertures and
102
windows on east and west sides, (4) shaping the building as narrow as possible with the shorter
103
side facing west and east, (5) providing vegetation surrounding the building, and (6) insulating
104
the external walls. Belleri et al. [41] compared natural ventilation rates predicted by an
105
EnergyPlus model to field study measurements and identified several key parameters that can
106
improve the accuracy of model predictions, including: occupant behavior, wind-speed profile,
107
internal heat gains, envelope conductivity, and wind pressure coefficients. Mora-Pérez et al. [42]
108
developed a computational fluid dynamic (CFD) model for selecting the best building location
109
that improves its natural ventilation performance by analyzing wind paths around and through
110
the building.
111
Fourth, several studies focused on optimizing the performance of natural and hybrid
112
ventilated buildings. For example, Deblois and Ndiaye [43] implemented a multivariable
113
optimization model to optimize the design of HVS in four elementary classrooms by maximizing
114
their occupied hours that utilize natural ventilation. Malkawi and Wang [44] developed a
115
methodology that combines genetic algorithms, CFD and network airflow models to optimize the
116
building form in order to maximize its natural ventilation potential in an urban environment. Guo
117
et al. [45] developed a methodology for optimizing site planning, building shape, and building
118
envelope of naturally-ventilated buildings. Rinaldi et al. [46] used a particle swarm optimization
119
method to develop a control strategy of windows opening in order to minimize the thermal
120
discomfort hours in hybrid ventilated residential buildings. Wang and Wang [47] developed an
121
intelligent control system for HVS in energy-efficient buildings that achieves an acceptable
122
indoor air quality while reducing energy consumption, by adjusting building ventilation rates
123
based on indoor CO2 concentration forecasts. Hamdy et al. [48] compared the performance of
124
seven commonly used multi-objective evolutionary optimization algorithms in solving design
125
problems of nearly zero energy buildings that utilize HVS and concluded that the two-phased
126
optimization using genetic algorithm provided the best performance among the analyzed seven
127
algorithms. Despite the significant contributions of the aforementioned research studies, they are
128
all incapable of (1) maximizing occupant satisfaction with human bioeffluents/body odor levels
129
in education buildings that utilize NVS or HVS; and (2) minimizing the construction cost of
130
these types of buildings; and (3) generating and analyzing optimal trade-offs between these two
131
important design objectives of education buildings.
132
2. Objective
133
The objective of this paper is to develop a model that optimizes the design of the
134
classroom space of naturally-ventilated education buildings that is capable of maximizing their
135
occupant satisfaction with human bioeffluents/body odor levels, minimizing their construction
136
cost, and generating optimal trade-offs between these two design objectives. The scope of the
137
model focuses on optimizing classroom spaces in education buildings and does not optimize the
138
design of other building spaces such as offices, cafeteria, library, and gymnasium. The multi-
139
objective optimization model is developed in three main stages: (1) model formulation stage that
140
identifies relevant design variables, objective functions and constraints; (2) model
141
implementation stage that executes the optimization computations; and (3) model evaluation
142
stage that analyses the performance of the developed model using an application example, as
143
shown in Fig. 1. The following sections describe in more detail these three development stages
144
of the multi-objective optimization model.
145 146
Fig. 1.
Model development
147
3. Model formulation
148
The present model was formulated in three main steps: (1) identifying the design
149
variables for the model; (2) defining the objective functions for the multi-objective optimization
150
model; and (3) formulating the model constraints.
151
3.1 Design variables
152
The model integrates ten design variables that represent the design decisions of education
153
building that have significant impact on (1) occupant satisfaction with human bioeffluents/body
154
odor levels, and (2) building construction cost as shown in Fig. 1. First, these ten design
155
variables directly affect CO2 concentration levels in classroom spaces and accordingly they have
156
significant impact on their occupant satisfaction with human bioeffluents/body odor levels.
157
Second, these ten design variables have significant impact on the building construction cost. The
158
possible selection of each of these ten design variables and their impact on the two optimization
159
objectives of the developed model are described in the following section.
160
Classroom layout selection (Lfw,c): represents the selected classroom layout from a set of
161
feasible alternatives for education buildings with atriums. Naturally-ventilated buildings often
162
require the use of an atrium to promote natural temperature stratification to increase buoyancy-
163
driven airflows [29], and their layout can be classified based on the atrium location as
164
centralized, semi-enclosed, linear, or attached as shown in Fig. 2 [49]. Each of these feasible
165
building layouts organizes the building classroom space into a number of wings that ranges from
166
1 in the linear layout to 4 in the centralized layout (see Fig. 2). The classroom space within each
167
of these wings can be designed to accommodate different types of classrooms with varying
168
student capacities such as daycare rooms, classrooms, and lecture halls [17] as shown in Fig. 2.
169
This variable (Lfw,c) is designed to consider and optimize the impact of both the building layout
170
type (centralized, semi-enclosed, linear, or attached) and the types of classrooms that will be
171
allocated within each wing in all building floors, as shown in Fig. 2. Accordingly, Lfw,c is
172
modeled using an integer variable that represents the selected classroom type for each class (c) in
173
each wing (w) in each floor (f). The value of this integer variable (Lfw,c) can range from 1 to n to
174
represent the selection of each classroom type from a set of n feasible alternatives. For example,
175
the selection of a lecture hall (fifth classroom type) for the second classroom location (c=2) in
176
the third wing (w=3) of the first floor (f=1) is represented by this variable as Lf=1w=3, c=2 = 5, as
177
shown in Fig. 2a.
178 179
Fig. 2.
Classroom layout selection for atrium buildings.
180
Building orientation (O): represents the azimuth angle in degrees between the true north
181
and the building direction perpendicular to the ventilated exterior wall of the building that has
182
ventilation openings and is considered to be the façade of wing A in this model that has the
183
longer length of the building, as shown in Fig. 3. This variable is designed to consider and
184
optimize the impact of building orientation on the natural-ventilation airflows driven by wind.
185
For example, a building orientation of zero (O = 0o) represents that wing A of the building faces
186
the true North direction.
187 188
Fig. 3.
Model design variables.
189
Floor height (FH): represents the height in meters of each floor of the building and is
190
used in the model to calculate the volume of each classroom, as shown in Fig. 3. FH is designed
191
to account for and optimize the impact of: (1) classroom volume on CO2 concentration over
192
time; (2) the position and height of building openings on buoyancy-driven airflows; and (3) floor
193
height on building cost.
194
Ventilation shaft height (SH): represents the vertical distance in meters from the roof of
195
the building to the roof of the atrium, as shown in Fig. 3. SH is designed to consider and
196
optimize the effect of the atrium height on buoyancy-driven natural ventilation (stack ventilation)
197
by inducing further temperature (and pressure) difference along the atrium. SH also impacts the
198
building cost.
199
Atrium width (AW): represents the minimum width of the atrium in meters, as shown in
200
Fig. 3. AW is designed to account for and optimize the effect of atrium volume on both the
201
natural ventilation and cost of the building.
202
Vents length (VLj): represents the length of vents located in wing (j) and is expressed as a
203
percentage of the classroom ventilated-wall length, as shown in Fig. 3. This percentage of
204
classroom ventilated-wall length (VLj) is allowed in the present model to exceed 100% to
205
provide multiple vents. For example, a solution of VLj = 160% represents double vents that
206
cover 80% of the ventilated-wall length. VLj is designed to search for and identify the size of
207
classroom vents to maximize natural ventilation airflows. It should be noted that the model
208
assumes in its calculation of CO2 levels the most conservative case when ventilation is provided
209
only through vents and all windows are closed. Opening any of these windows will produce
210
additional ventilation and further reduction in CO2 concentration and human bioeffluents/body
211
odor levels.
212
Window to wall ratio of classrooms (WWRc): represents the ratio between the glazed
213
area to the total area of the ventilated wall in each classroom, as shown in Fig. 3. WWRc is
214
designed to consider and optimize the impact of fenestration on the classroom air temperature
215
due to the heat gains by solar radiation and conduction through the glazing. Temperature
216
difference between adjoining spaces (e.g., outdoor, classrooms and atrium) affects buoyancy-
217
driven airflows.
218
Window to wall ratio of the atrium (WWRa): represents the ratio between the atrium’s
219
fenestration area and the exterior wall area excluding the wall area above the building roof level,
220
as shown in Fig. 3. WWRa is designed to consider and optimize the effect of fenestration on heat
221
gains in the atrium to enhance its stack ventilation.
222
Window to wall ratio of the shaft (WWRs): represents the ratio between the glazing area
223
in the roof and walls of the ventilation shaft and the total envelope area of the shaft, as shown in
224
Fig. 3. WWRs is designed to consider and optimize the effect of glazing on the walls and roof of
225
the ventilation shaft to enhance buoyancy-driven airflows through the atrium by generating a
226
solar chimney effect.
227
Occupancy density of classroom (ODi,j): represents the maximum occupant density of
228
each type of classroom (i) in each wing (j) of the building, represented by the number of
229
occupants per 100 square meters of classroom area. The ODi,j is designed to account for and
230
optimize the effect of classroom density on CO2 concentration levels inside the classroom.
231
3.2 Objective functions
232
The model incorporates two optimization objective functions that are designed to (1)
233
maximize the occupant satisfaction with human bioeffluents/body odor levels, and (2) minimize
234
the construction cost of classroom space in education buildings. It should be noted that these two
235
optimization objectives are often conflicting because improvements in the first objective function
236
can be achieved by increasing classroom space and height which have a negative impact on the
237
performance of the construction cost objective function. Accordingly, the model is designed to
238
support multi-objective optimization to enable designers to search for and identify building
239
designs that provide optimal trade-offs between these two conflicting objectives.
240
3.2.1 Maximizing occupant satisfaction with human bioeffluents/body odor levels
241
(OS)
242
The first objective function in the model is designed to calculate and optimize occupant
243
satisfaction with human bioeffluents/body odor levels (OS) of classrooms in naturally-ventilated
244
buildings. The performance of OS in this model is measured in terms of the percentage of time
245
that classrooms provide acceptable human bioeffluents/body odor levels for their occupants
246
during the analysis period. ASHRAE [17] defines acceptable IAQ as “air in which there are no
247
known contaminants at harmful concentrations as determined by cognizant authorities and with
248
which a substantial majority (80% or more) of the people exposed do not express
249
dissatisfaction”. Ventilation-related contaminants that are reported to cause occupant
250
dissatisfaction and can be controlled by ventilation are carbon dioxide (CO2) and human body
251
odor emitted by occupants [17,50]. Other contaminants such as formaldehyde, VOC, lead, PM,
252
radon that are listed in Appendix B in ASHRAE Standard 62.1 [17] are controlled more
253
efficiently using source control strategies such as selecting low-emitting materials for
254
construction, furniture and cleaning.
255
Improved ventilation has been reported by many studies to reduce the negative impacts
256
of the CO2 and human body odor contaminants. These studies showed that a ventilation rate of
257
7.5 L/s per person of outdoor air enables 80% of unadapted persons (visitors) to find human
258
body odor at an acceptable level [51–55]. The same level of body odor acceptability is achieved
259
when the difference between the indoor and outdoor CO2 levels is less than or equal to 650 ppm
260
[15]. This correlation between CO2 concentration and dissatisfaction with bioeffluent odor is
261
used in the ventilation requirements in existing standards and guidelines [15,17,56].
262
Accordingly, the present model quantifies and measures the performance of the overall
263
satisfaction with human bioeffluents/body odor levels of building occupants in two steps that are
264
designed to: (1) calculate the concentration levels of carbon dioxide (CO2) in all classrooms, and
265
(2) estimate the percentage of the time that classrooms provide acceptable occupant satisfaction
266
based on their calculated CO2 levels.
267
In the first step, the model calculates CO2 concentration in each classroom by simulating
268
the natural ventilation of the building during a whole calendar year using: (a) CONTAM [57],
269
which is a widely-used multizone building airflow and contaminant transport simulation tool;
270
and (b) EnergyPlus [58], which is a whole-building energy simulation program, as shown in Fig.
271
7. Both simulation tools are coupled using a quazi-dynamic method [28] to perform building co-
272
simulation. CONTAM is used to generate a network airflow model of the building to estimate
273
indoor (interzone) and outdoor (natural ventilation) airflows required by EnergyPlus and to
274
perform a mass balance analysis to compute CO2 levels in each building zone (classrooms and
275
atrium). EnergyPlus, on the other hand, is used to perform heat transfer calculations to compute
276
indoor temperature required by CONTAM to calculate buoyancy-driven airflows. This
277
CONTAM-EnergyPlus co-simulation is used in the present model to calculate the changes in the
278
CO2 levels over an entire calendar year in each classroom, as shown in the example classroom
279
CO2 variations over one year in Fig. 4a and one day in Fig. 4b.
280 281 282
Fig. 4.
Example of calculated CO2 levels variations over (a) one year, and (b) one day in one classroom.
283
In the second step, the CO2 levels calculated in the previous step are used to estimate the
284
average OS in all classrooms in the education building over an entire calendar year in three sub-
285
steps that are designed to calculate (1) OSc,d in classroom (c) for each school day (d), as shown in
286
Eq. 1; (2) average OSc in each classroom (c) for an entire calendar year (d = 1 to D), as shown in
287
Eq. 2; and (3) average OS in all classrooms in the education building for an entire calendar year,
288
as shown in Eq. 3. In the first sub-step, the model calculates OSc,d by identifying the percentage
289
of the time that students experience an acceptable human bioeffluents/body odor levels during
290
their occupancy of classroom (c) in school day (d). This OSc,d percentage is calculated as the
291
ratio between (1) total daily time that the classroom has acceptable levels of CO2, and (2) total
292
time of a school day. The total daily time of acceptable CO2 levels is calculated as the sum of the
293
durations of all timesteps (tc,d,s) that comply with designer-specified acceptable CO2 levels, as
294
shown in Fig. 5, the designer-specified acceptable CO2 level is assumed in the application
295
example to be 1000 ppm based on an assumed CO2 level of 350 ppm in outside air and the
296
reference value provided by ASTM standard D6245 of 650 ppm above outdoor levels [15]. The
297
total time of a school day is determined by the daily occupied class time that starts at timestep
298
(B) and ends at timestep (F), as shown in Fig. 5 and Eq. 1. The second and third sub-steps are
299
then used to calculate the average OS(c) in each classroom (c) for an entire calendar year and the
300
average OS in all classrooms in the education building during a calendar year, as shown in Eq. 2
301
and Eq. 3, respectively.
,
% =
, ,
−
+1 ∗ ,
% = !
% =
"
,
(1)
∗ 100 (2)
(3)
302
Where tc,d,s is the amount of time in seconds that simulation timestep (s) of day (d) of
303
classroom (c) has a calculated CO2 level equal than or below to the specified acceptable CO2
304
level of 1000 ppm, as shown in the example on Fig. 5; T is the duration in seconds of each
305
simulation timestep; B is the timestep when classes begin each day following the occupancy
306
schedule defined for the co-simulation; F is the timesteps when classes finish each day; D is the
307
total number of days in the co-simulation period which is assumed to be an entire calendar year
308
in this model; and C is the total number of classrooms in the building.
309 310
Fig. 5.
311
3.2.2 Minimizing construction cost (CC)
Example of calculation of OSc,d in classroom (c=11) on March 28th (d=87)
312
The second objective function in the model is designed to calculate and minimize the
313
construction cost (CC) of classroom space in education buildings. This cost (CC) is computed
314
using square foot cost models for green institutional buildings that are developed by RSMeans
315
(2018). Accordingly, this cost (CC) is calculated by aggregating the cost of the major group of
316
construction elements of substructure, shell, interiors, services, equipment and furnishings,
317
special construction, and building sitework based on the UNIFORMAT II classification system
318
[60], as shown in Eq. 4.
=#
$%&
∗
+
$'())
6
+
*+,
+
$(-.
+
/0&2
+
$3
+
4$ 5 ∗
1+
(4)
319
Where, CSub is the assembly cost estimate of the building substructure; CShell is the
320
assembly cost estimate of the building shell; CInt is the assembly cost estimate of the building
321
interiors; CServ is the assembly cost estimate of the building services; CEq&F is the assembly cost
322
estimate of the building equipment and furnishings; CSC is the assembly cost estimate of the
323
building special construction; CBS is the assembly cost estimate of the building sitework; CF
324
represents the contractor overhead and profit percentage; and CI represents the city index used to
325
adjust the building cost estimates to a specific location.
326
The cost of each of the aforementioned seven major groups of construction elements is
327
estimated by aggregating the cost of all its individual elements that are listed in Table 1. Each of
328
these individual element costs is estimated by multiplying its assembly unit cost by its number of
329
units calculated by the model based on the building design solution. For example, the cost of
330
individual element “A1030 Slab on grade” is estimated by multiplying the assembly unit cost of
331
a “4 in reinforced concrete slab with recycled vapor barrier and granular base” that is equal to
332
$5.84 per square foot [59] by its quantity take-off equal to 8,740.30 square feet as shown in Fig.
333
6. The cost of the remaining individual elements of the building are estimated using a similar
334
approach.
335 336 337 338
339 340
Table 1.
Building elements breakdown for model G.580 School, Jr High [59]
Level 1 Major group elements A Substructure (CSub)
Level 2 Group elements A10 Foundation
A20 Basement Construction B Shell (CShell)
B10 Superstructure B20 Exterior enclosure
B30 Roofing C Interiors (CInt)
C10 Interior construction C20 Stairs C30 Interior finishes
D Services (CServ)
D10 Conveying D20 Plumbing
D30 HVAC
D40 Fire protection D50 Electrical
E Equipment and furnishings (CE&F)
E10 Equipment E20 Furnishing
341
Level 3 Individual elements A1010 Standard foundation A1030 Slab on grade (see example in Fig. 6) A2010 Basement excavation A2020 Basement walls B1010 Floor construction B1020 Roof construction B2010 Exterior walls B2020 Exterior windows B2030 Exterior doors B3010 Roof coverings B3020 Roof openings C1010 Partitions C1020 Interior doors C2010 Stair construction C3010 Wall finishes C3020 Floor finishes C3030 Ceiling finishes D1010 Elevators & lifts D2010 Plumbing fixtures D2020 Domestic water distribution D2040 Rainwater drainage D3040 Distribution system D3020 Heat generating system D3050 Terminal & package units D4010 Sprinklers D4020 Standpipes D5010 Electrical service/distribution D5020 Lighting & branch wiring D5030 Other equipment D5090 Other electrical systems E1020 Institutional equipment E1090 Other equipment E2020 Moveable furnishings
342 343 344
Fig. 6.
Example of cost calculation of individual element A1030 Slab on grade.
3.3 Constraints
345
The developed model is designed to comply with three types of constraints: design
346
variables constraints, budget constraint, and residual space constraint. The model constraints are
347
set to ensure practical solutions, reduce the design and solution spaces, and decrease the model
348
computation time.
349
Design variable constraints: This constraint provides building designers with the
350
flexibility to specify a practical range for each design variable that can vary from one project to
351
another. The model is formulated to analyze all alternative design solutions within that designer-
352
specified range in order to identify an optimal solution for each design variable. For example, a
353
designer can specify that the window to wall ratio of classrooms (WWRc) can range from 20%
354
to 80% with an increment of 1%. The model is designed to comply with this constraint by
355
generating and analyzing all alternative design solutions that are limited by that range. The
356
constraints of the remaining design variables can be specified by designers using a similar
357
approach.
358
Budget constraint (Bmax): This constraint represents the owner-specified maximum
359
budget that can be allocated to the project. The budget constraint is designed to reduce the
360
solution space and computational time of the model by discarding non-complying solutions
361
before the evaluation of the OS objective function, as shown in Fig. 7.
362
Residual space constraint (RSmax): This constraint represents the designer-specified
363
maximum residual space allowed in a feasible design solution. The residual space represents a
364
space filler that is often needed to be placed in one of the building wings to equalize the length of
365
opposed building sides in order to produce a building with a rectangular shape. Although the
366
residual space is reduced during the optimization as a byproduct of minimizing the construction
367
cost, the present model provides designers with the flexibility to specify an upper limit on this
368
variable based on the specific conditions of their project.
369
4. Model implementation
370
The proposed model is implemented using multi-objective non-dominated sorting genetic
371
algorithm II NSGAII [61] due to their capabilities to generate optimal/near-optimal trade-offs
372
among optimization objectives and to model nonlinear and discontinuous objective functions.
373
The optimization model is developed using Visual Basic and combined with a multizone
374
building airflow and contaminant transport simulation tool, CONTAM, and an external building
375
simulation engine, EnergyPlus. The optimization computations are performed in three modules:
376
(1) initialization module which enables designers to specify the values of all required input data;
377
(2) optimization module which generates an initial population, ranks the generated solutions,
378
produces subsequent generations using the genetic algorithm operators, and identifies optimal
379
trade-off solutions between the occupant satisfaction with human bioeffluents/body odor levels
380
and construction cost objective functions; (3) objective function module which calculates the
381
occupant satisfaction with human bioeffluents/body odor levels and construction cost for each of
382
the generated solutions using two external simulation tools (CONTAM and EnergyPlus), as
383
shown in Fig. 7.
384
4.1 Initialization module
385
The purpose of this module is to enable designers to specify all the required project input
386
data. This input data are classified in 10 categories: (1) weather data that represents average
387
weather conditions in the project location for an entire calendar year that is required by the
388
external building energy simulation program EnergyPlus; (2) classroom data that includes for
389
each type of classroom in the building its required number, planned number of occupants, and
390
side ratio; (3) building data that includes its required type of atrium as well as the minimum and
391
maximum number of classrooms per building wing; (4) daily schedule of classroom occupancy;
392
(5) construction cost data for all the individual building elements shown in Table 1; (6)
393
CONTAM simulation tool parameters that specifies simulation period, simulation timestep
394
duration, CO2 generation rate of occupants, airflow parameters to model the building openings,
395
relative height and length of the wall openings, and; (7) EnergyPlus simulation program
396
parameters that includes the construction material properties and heat gains from equipment and
397
lighting; (8) design variable constraints that specifies the minimum and maximum value of each
398
design variable and its increment; (9) budget (Bmax) and residual space (RSmax) constraints; and
399
(10) NSGAII algorithm parameters that specifies population size (S), maximum number of
400
generations (G), recombination probability (Pc), and mutation probability (Pm).
401
4.2 Optimization module
402
The purpose of this module is to identify the Pareto front of optimal or near-optimal
403
trade-off solutions between the OS and CC objective functions. To achieve this, the
404
computational procedure in this module is implemented in nine tasks that are designed to: (1)
405
generate an initial population (Pg=1) with (S) random solutions; (2) calculate the value of the two
406
objective functions for each solution in the initial population (Pg=1) using the objective function
407
module; (3) sort and rank all solutions in the initial population (Pg=1) based on their calculated
408
objective functions using the Pareto dominance and crowding distance criteria; (4) generate child
409
population (Cg) using tournament selection, recombination and mutation; (5) calculate the value
410
of the two objective functions for each solution in the child population (Cg) using the objective
411
function module; (6) create a new combined population (Ng) that combines the parent (Pg) and
412
child populations (Cg); (7) sort and rank all solutions in the new combined population (Ng = Pg +
413
Cg) using the Pareto dominance and crowding distance criteria; (8) select the top (S) solutions
414
from Ng to generate a new parent population (Pg+1); (9) repeat tasks (4) to (8) until the maximum
415
generation (G) is reached; and (10) identify the Pareto optimal front based on the results of the
416
last generation (PG).
417
4.3 Objective function module
418
The main purpose of this module is to calculate the OS and CC objective functions for
419
each solution (s) in the initial population (P1) and subsequent Child populations (Cg) to evaluate
420
their fitness. The fitness of each solution enhances its rank in the population by increasing its
421
chances to survive and be recombined in the next generation. The computational procedure in
422
this module is implemented in six tasks that are designed to: (1) generate a building design based
423
on the selected values for its design variables; (2) calculate the residual space (RS) of the
424
generated building design which represents a space filler that is often needed to be placed in one
425
of the building wings to equalize the length of opposed building sides in order to produce a
426
building with a rectangular shape; (3) compute the construction cost (CC) objective function
427
using Eq. 4; (4) verify if the generated building solution complies with both the budget constraint
428
(CC ≤ Bmax) and residual space (RS ≤ RSmax) constraints; (5) discard solutions that do not
429
comply with both constraints; (6) generate simulation files for all solutions that comply with both
430
constraints: CONTAM input file (prj file), EnergyPlus input file (idf file), and coupled
431
simulation data exchange files (contam.vef, and modelDescription.xml) [28]; (7) execute the
432
CONTAM-EnergyPlus coupled simulation; and (8) compute the OS objective function from the
433
CONTAM output file (sim file) using Eq. 3.
434 435 436
Fig. 7.
Optimization model implementation using NSGAII.
437
5. Performance evaluation
438
An application example of a school building is analyzed to illustrate the capabilities of
439
the developed model and evaluate its performance in generating optimal trade-offs between the
440
occupant satisfaction with human bioeffluents /body odor levels and the building construction
441
cost. The project design input data for this education building example is specified to have: (1)
442
weather data based on its location in Los Angeles, CA; (2) 12 classrooms (c=12) that have
443
varying design requirements as shown in Table 2; (3) a linear atrium with two to four classrooms
444
per building wing; (4) a daily schedule of four classes that has a duration of one hour and 45
445
minutes each and are separated by 15 minutes recesses (see Fig. 4b), with an occupancy rate of
446
100% during class time and 10% during recess; (5) construction cost data, as shown in Tables 3
447
and 4; (6) CONTAM simulation tool parameters that specifies simulation to be performed for an
448
entire year using four timesteps per hour (T=900 s), CO2 generation rate of 17.28 liters per hour
449
per occupant [56], and assuming that each classroom has vents located at 0.3 of the floor height,
450
where each is capable of providing an airflow rate of 34.2 l/s/m at 1 Pa; (7) EnergyPlus
451
simulation program parameters that assumes that envelope materials comply with standard
452
ASHRAE 189.1-2014 and internal heat gains from equipment and lighting are estimated to be
453
24.3 W/m2 of floor area; (8) design variable constraints as shown in Table 5; (9) budget and
454
residual space constraints that are specified to be less than or equal $6 million and 160 m2,
455
respectively; (10) NSGAII algorithm parameters are specified to be 320 generations, initial
456
population of 400 random solutions, subsequent child populations of 40 solutions, crossover
457
probability of 85%, and a mutation rate of 5% [62,63].
458
459
Table 2.
Required classroom types for application example.
Classroom type Quantity Capacity [Persons] Sides Ratio (1:x)
460 461
Table 3.
1
2
3
4
5
2 20 1.5
4 25 1.5
4 40 1.8
1 65 1.5
1 80 1.8
Application example construction cost data for model G.580 School
462
(RSMeans 2018). Individual elements A1010 Standard foundation A1030 Slab on grade A2010 Basement excavation A2020 Basement walls B1010 Floor construction B1020 Roof construction B2010 Exterior walls*
B2020 Exterior windows*
B2030 Exterior doors B3010 Roof coverings*
B3020 Roof openings*
C1010 Partitions C1020 Interior doors C2010 Stair construction C3010 Wall finishes C3020 Floor finishes C3030 Ceiling finishes D1010 Elevators & lifts D2010 Plumbing fixtures
Assembly items Poured concrete; strip and spread footings 4” reinforced concrete with recycle vapor barrier and granular base Site preparation for slab and trench for foundation wall and footing 4” foundation wall Open web steel joists, slab form, concrete, columns Metal deck, open web steel joist, columns Face brick with concrete block backup and 2 in of EPS (R-1.35) continuous insulation (total assembly U-0.4809) Double pane window, 6 mm clear glasses with a hi-reflective coating in one surface (U2.864, SHGC =0.247 and VT=0.881) Wall vents Double aluminum & glass Single-ply TPO membrane & standing seam metal with 6.75 in of EPS (R-4.57) insulation (total assembly U-0.2096) Skylight with the same glass than exterior window Roof ventilators Concrete block w/foamed-in insulation Single leaf kalamein fire doors, low VOC paint Concrete filled metal pan 50% paint, low VOC, 40% glazed coatings, 10% ceramic tile 50% vinyl comp. tile, recycled content, 30% carpet tile, 20% terrazzo Mineral fiberboard on concealed zee bars One hydraulic passenger elevator Low flow, auto sensor, service fixtures, supply and drain (1 fixture per 1170 SF Floor)
Assembly unit cost $2.72 $5.84
per SF Ground per SF Slab
$0.18
per SF Ground
$98.00 $30.22
per LF Wall per LF Floor
$12.58 $33.49
per SF Roof per SF Wall
$78.69
per SF Fenestration
$60.96 $7,200.00 $6.05
per LF Vents per Each per SF Roof
$113.86
per SF Skylight per LF Vents per SF Partitions per Each
$457.20 $14.95 $1,222.00 $15,800.00 $4.04 $9.24 $7.60 $91,300.00 $7,675.00
per SF Floor per SF Surface per SF Floor per SF Ceiling per Each per Each
463
Table 4.
Application example construction cost data (cont’d).
Individual elements D2020 Domestic water distribution D2040 Rainwater drainage D3040 Distribution system D3050 Terminal & package units D4010 Sprinklers D4020 Standpipes D5010 Electrical service/distribution D5020 Lighting & branch wiring D5030 Other equipment D5090 Other electrical systems E1020 Institutional equipment E1090 Other equipment
464 465 466
467
Assembly items
Assembly unit cost
Gas fired, tankless water heater Roof drains Enthalpy heat recovery packages Multizone rooftop air conditioner SEER 14 (includes heat generating system) Sprinklers, light hazard Standpipes, wet, Class III 1600 ampere service, Panel board and feeders LED fixtures, daylight dimers, light on/off/ receptacles, switches, and A.C. power Addressable alarm system, internet wiring, communication systems and emergency light Emergency generator, 100 kW, and energy monitoring systems Laboratory casework and counters
$0.38
per SF Floor
$2.02 $38,725.00 $20.20
per SF Roof per Each per SF Floor
$2.57 $0.45 $0.75
per SF Floor per SF Floor per SF Floor
$13.28
per SF Floor
$5.11
per SF Floor
$0.80
per SF Floor
$2.65
per SF Floor
Waste handling recycling tilt truck, built-in $1.35 per SF Floor athletic equipment, bleachers & backstops E2020 Moveable furnishings No smoking signage $0.02 per SF Floor * Cost rates adjusted to comply with Standard 189.1-2014 (SI) for non-residential building in climate zone 3
Table 5.
Application example design variable constraints.
Design variable
Min. Value
Max. Value
Increment
Possible options
Classroom layout selection (L) Building Orientation (O) Floor height (FH) Ventilation shaft height (SH) Atrium width (AW) Vents length (VL1 and VL2) Window to wall ratio of classrooms (WWRc) Window to wall ratio of the atrium (WWRa) Window to wall ratio of the shaft (WWRs) Occupancy density of classroom 1 (OD1,1 and OD1,2) Occupancy density of classroom 2 (OD2,1 and OD2,2) Occupancy density of classroom 3 (OD3,1 and OD3,2) Occupancy density of classroom 4 (OD4,1 and OD4,2) Occupancy density of classroom 5 (OD5,1 and OD5,2)
1 0⁰ 2.8 m 0.5 m 5m 80% 20% 10% 0% 19 19 26 49 60
5 359⁰ 4.5 m 3.0 m 8m 160% 90% 90% 90% 25 25 35 65 80
1 1⁰ 0.1 m 0.1 m 1m 1% 1% 1% 1% 1 1 1 1 1
20,432 360 18 26 4 81 71 81 91 7 7 10 17 21
468
The aforementioned specified project input data for this application example creates a
469
solution space that includes 1.4x1030 feasible alternative solutions which is calculated as the
470
product of multiplying the possible combinations of all the possible options of the design
471
variables in Table 5. Each of these solutions provides an alternative building design that delivers
472
a unique OS and construction cost for the education building. Designers who are trying to
473
maximize the occupant satisfaction with human bioeffluents/body odor levels of this building
474
while keeping its construction cost to a minimum need to evaluate the impact of various building
475
designs on these two important criteria. Analyzing the OS and cost performance of all these
476
1.4x1030 feasible alternatives to identify an optimal design is impractical due to its prohibitive
477
computational time and effort. To support building designers in this challenging task, the
478
developed model is used to optimize the design of this application example in order to generate
479
and analyze optimal trade-offs between its two optimization objectives of maximizing OS and
480
minimizing construction cost. The model was able to generate 137 non-dominated near-optimal
481
solutions, where each represents a unique and optimal trade-off among the two objective
482
functions, as shown in Fig. 8. This wide range of optimal tradeoffs between the OS objective and
483
construction cost objective includes two extreme solutions (a and b) that are highlighted in Fig.
484
8. The first extreme solution (a) provides the highest OS of 98.39% at a construction cost of
485
$5,718,636, while the second extreme solution (b) provides the least construction cost of
486
$3,573,381 with an OS of 54.03% (see Fig. 8 and Table 6).
487 488 489
490 491 492
Fig. 8.
Optimal trade-offs between the construction cost and occupant satisfaction with human bioeffluents/body odor levels for the school building example.
Fig. 9.
Representative solutions of the application example.
493
Table 6.
Sample of optimal non-dominated solutions.
Design variables
Solution (a)
Solution (b)
Solution (c)
(See. Fig 10a)
(See. Fig 10b)
(See. Fig 10c)
25 m
27 m
23 m
Building length
40 m
30 m
39 m
Building Orientation (O) Floor height (FH)
166⁰ 4.5 m
51⁰ 2.8 m
51⁰ 2.8 m
Ventilation shaft height (SH)
3.0 m
0.5 m
3.0 m
Atrium width (AW) Vents length (VL1 and VL2)
5m 86 m, 68 m
5m 51 m, 49 m
5m 66 m, 63 m
Classroom layout selection (L) Building width
Window to wall ratio of
classrooms (WWRc)
83%
21%
21%
the atrium (WWRa) the shaft (WWRs)
79% 78%
11% 0%
89% 0%
Occupancy density of classroom
1 (OD1,1 and OD1,2)
25, 25
24, 21
25, 24
2 (OD2,1 and OD2,2) 3 (OD3,1 and OD3,2)
25, 20 35, 33
25, 20 32, 35
24, 20 32, 35
4 (OD4,1 and OD4,2)
56, 56
62, 62
57, 57
5 (OD5,1 and OD5,2)
72, 72
80, 80
80, 80
98.39% $5,718,636
54.03% $3,573,381
90.06% $4,055,775
Occupant satisfaction with human bioeffluents levels Construction cost
494
495 496
Fig. 10.
Classroom layout selection for solutions (a), (b) and (c)
497
The first extreme solution (a) in the generated Pareto optimal front was able to achieve
498
the maximum OS (98.39%) for the education building example by maximizing natural
499
ventilation airflows and size of classrooms to slow the CO2 accumulation over time while
500
keeping construction cost to a minimum. As shown in Fig. 9 and Table 6, this was achieved by
501
(1) selecting a classroom layout that places 61% of the school students in wing A of the building
502
that has better natural ventilation due to the orientation of the building and the prevailing wind
503
direction; (2) selecting a building orientation of 166⁰ that maximize the stack ventilation; (3)
504
increasing floor height to 4.5 m to maximize the volume of indoor air in classroom volumes and
505
the stack effect in the building; (4) raising the height of the ventilation shaft to 3 m to increase
506
the stack effect; (5) reducing the width of the atrium to its minimum value (5 m) which raises its
507
temperature to facilitate buoyancy driven airflows; (6) selecting a large vent length of 85.6 m m
508
in wings A and 68 m in wing B of the building to maximize its natural ventilation; (7) increasing
509
the windows to wall ratios of classrooms, atrium and shaft (83, 79%, and 78%, respectively) to
510
increase difeerences between indoor and outdoor temperatures to enhance bouancy driven
511
airflows; (8) reducing overall classroom occupancy densities of the building to 30.4 occupants
512
per 100 m2 to minimize CO2 concentrations in classrooms.
513
On the other extreme of the generated optimal trade-off solutions, solution (b) was able to
514
achieve the lowest construction cost ($3,485,507) by: (1) selecting a building orientation of 51⁰
515
that enables the high density classrooms in wing B to face the prevailing wind direction in this
516
geographical location to improve their wind-driven natural ventilation; (2) reducing building
517
floor height to its minimum allowed limit of 2.8 m to reduce the building construction cost; (3)
518
lowering the height of the ventilation shaft to 0.5 m to reduce its construction cost; (4)
519
minimizing the atrium width to 5 m to reduce construction costs; (5) reducing the length of
520
vents in Wings A and B to 51 m, and 49 m, respectively to reduce their cost; (6) decreasing the
521
windows to wall ratios of classrooms, atrium, and shaft to 21%, 11%, and 0%, respectively to
522
minimize the use of windows and their cost in the building; and (7) increasing overall classroom
523
occupancy densities of the building to 35.2 occupants per 100 m2 to minimize classroom space
524
and their construction cost, as shown in Fig. 9 and Table 6.
525
In addition to the two aforementioned extreme solutions, the optimization model was able
526
to generate 135 other trade-off solutions, including solution (c). This solution generated an OS
527
of 90.06%, which is lower than solution (a) performance of 98.39%; however, it provides a
528
lower construction cost of $4,055,775 compared to that of solution (a) that had a cost of
529
$5,718,636. This performance of solutions (c) was achieved by selecting an optimal set of
530
solutions for the design variables, as shown Fig. 9 and Table 6. This illustrates the capability of
531
the developed optimization model to generate a wide range of optimal trade-offs solutions, where
532
each provides a unique and optimal trade-off between the occupant satisfaction with human
533
bioeffluents/body odor levels and their construction cost, as shown in Fig. 8. This enables
534
designers to generate and analyze these optimal trade-offs and accordingly identify an optimal
535
set of design decisions that strikes an optimal balance between the two conflicting optimization
536
objectives considered in the developed model. Furthermore, the application example results
537
clearly illustrate the impact of the education building design decisions on its occupant
538
satisfaction with human bioeffluents/body odor levels and cost and the need for designers to
539
consider and optimize these impacts during the design of naturally-ventilated education
540
buildings.
541
6. Summary and Conclusions
542
The paper presented the development of a multi-objective optimization model for
543
optimizing the design of naturally-ventilated education buildings in order to maximize their
544
occupant satisfaction with human bioeffluents/body odor levels while minimizing their building
545
construction cost. The multi-objective optimization model is developed in three main stages: (1)
546
model formulation stage that identifies relevant design variables, objective functions and
547
constraints; (2) model implementation stage that executes the optimization computations; and (3)
548
model evaluation stage that analyzes the performance of the developed model using an
549
application example of a school building. The results of this application example analysis
550
highlight the new and unique capabilities of the developed model in generating a wide range of
551
Pareto-optimal design solutions, where each provides a unique and optimal trade-off between
552
occupant satisfaction with human bioeffluents/body odor levels and construction cost of
553
education buildings.
554
The model was developed based on a number of assumptions, including: (1) outdoor air
555
quality in the educational building location is acceptable and does not include more contaminants
556
than indoor air; (2) the scope of the model is limited to naturally-ventilated education buildings
557
that do not integrate mechanical ventilation or HVAC systems; (3) the model minimizes only
558
building construction cost and does not consider other costs such as energy, productivity, health-
559
related, operation, and maintenance costs; (4) calculation of CO2 levels in classroom spaces
560
assumes the most conservative case when ventilation is provided only through vents and all
561
windows are closed; and (5) optimal window sizes are selected from a designer-specified range
562
of feasible sizes for each window that provide the required level of lighting in classrooms.
563
The primary contribution of this research to the body of knowledge include (a) a novel
564
methodology for measuring and quantifying the impact of the design decisions of naturally-
565
ventilated education buildings on their occupant satisfaction with human bioeffluents/body odor
566
levels and construction cost, and (b) an original multi-objective optimization model that is
567
capable of generating optimal trade-offs between these two critical design objectives. These new
568
and innovative capabilities are expected to improve current design practices of naturally-
569
ventilated education buildings and will contribute to maximizing their human bioeffluents/body
570
odor satisfaction of occupants while minimizing their construction cost. The scope of the
571
developed model can be expanded in future research to enable the consideration and
572
optimization of additional (i) costs such as energy, productivity, health-related, and maintenance
573
costs; and (ii) optimization objectives such as indoor air quality, thermal comfort, energy
574
consumption, and life cycle costs of education buildings to generate optimal trade-offs among
575
them.
576
Acknowledgement
577
This material is based upon work supported by the Universidad Panamericana, the
578
Consejo Nacional de Ciencia y Tecnología (CONACYT) and the ZJU-UIUC Institute Research
579
Program. Any opinions, findings, conclusions, or recommendations expressed in this publication
580
are those of the writers and do not necessarily reflect the views of Universidad Panamericana,
581
CONACYT and ZJU-UIUC Institute Research Program.
582
References
583
[1]
584 585
http://www.census.gov/hhes/school/data/cps/2014/tables.html (accessed April 6, 2016). [2]
586 587
USCB, Current Population Survey Data on School Enrollment: October 2014, (2014).
EIA, Commercial Buildings Energy Consumption Survey (CBECS 2012), 2012. http://www.census.gov/hhes/school/data/cps/2014/tables.html.
[3]
588
P. Mackun, S. Wilson, T. Fischetti, J. Goworowska, Population Distribution and Change: 2000 to 2010, 2011. doi:http://www.census.gov/prod/cen2010/briefs/c2010br-01.pdf.
589
[4]
DOE, Building Energy Data Book, 2011.
590
[5]
A. Ford, Designing the sustainable school, The Images Publishing Group, Victoria, 2007.
591
[6]
I. Sarbu, C. Pacurar, Experimental and numerical research to assess indoor environment
592
quality and schoolwork performance in university classrooms, Build. Environ. 93 (2015)
593
141–154. doi:10.1016/j.buildenv.2015.06.022.
594
[7]
O. Toyinbo, R. Shaughnessy, M. Turunen, T. Putus, J. Metsämuuronen, J. Kurnitski, U.
595
Haverinen-Shaughnessy, Building characteristics, indoor environmental quality, and
596
mathematics achievement in Finnish elementary schools, Build. Environ. 104 (2016) 114–
597
121. doi:10.1016/j.buildenv.2016.04.030.
598
[8]
M. Turunen, O. Toyinbo, T. Putus, A. Nevalainen, R. Shaughnessy, U. Haverinen-
599
Shaughnessy, Indoor environmental quality in school buildings, and the health and
600
wellbeing of students, Int. J. Hyg. Environ. Health. 217 (2014) 733–739.
601
doi:10.1016/j.ijheh.2014.03.002.
602
[9]
Z. Yang, B. Becerik-Gerber, L. Mino, A study on student perceptions of higher education
603
classrooms: Impact of classroom attributes on student satisfaction and performance, Build.
604
Environ. 70 (2013) 171–188. doi:10.1016/j.buildenv.2013.08.030.
605
[10]
Z. Bakó-Biró, D.J. Clements-Croome, N. Kochhar, H.B. Awbi, M.J. Williams, Ventilation
606
rates in schools and pupils’ performance, Build. Environ. 48 (2012) 215–223.
607
doi:10.1016/j.buildenv.2011.08.018.
608
[11]
J.M. Daisey, W.J. Angell, M.G. Apte, Indoor air quality, ventilation and health symptoms
609
in schools: an analysis of existing information, Indoor Air. 13 (2003) 53–64.
610
doi:10.1034/j.1600-0668.2003.00153.x.
611
[12]
P. Wargocki, D.P. Wyon, Ten questions concerning thermal and indoor air quality effects
612
on the performance of office work and schoolwork, Build. Environ. 11 (2017) 359–366.
613
doi:http://dx.doi.org/10.1016/j.buildenv.2016.11.020.
614
[13]
K.W. Tham, Indoor air quality and its effects on humans—A review of challenges and
615
developments
616
doi:10.1016/j.enbuild.2016.08.071.
617
[14]
U.
in
the
last
Haverinen-Shaughnessy,
30
R.J.
years,
Energy
Shaughnessy,
Build.
E.C.
130
Cole,
(2016)
O.
637–650.
Toyinbo,
D.J.
618
Moschandreas, An assessment of indoor environmental quality in schools and its
619
association with health and performance, Build. Environ. 93 (2015) 35–40.
620
doi:10.1016/j.buildenv.2015.03.006.
621
[15]
ASTM Standard D6245-18 Standard Guide for Using Indoor Carbon Dioxide
622
Concentrations to Evaluate Indoor Air Quality and Ventilation, West Conshohocken, PA,
623
2018.
624
[16]
L. Chatzidiakou, D. Mumovic, A. Summerfield, Is CO2 a good proxy for indoor air
625
quality in classrooms? Part 1: The interrelationships between thermal conditions, CO2
626
levels, ventilation rates and selected indoor pollutants, Build. Serv. Eng. Res. Technol. 36
627
(2015) 129–161. doi:10.1177/0143624414566244.
628
[17]
629 630
ANSI/ASHRAE Standard 62.1-2016 Ventilation for Acceptable Indoor Air Quality, Atlanta, GA, 2016.
[18]
S.J. Emmerich, Simulated Performance of Natural and Hybrid Ventilation Systems in an
631
Office
Building,
HVAC&R
632
doi:10.1080/10789669.2006.10391447.
Res.
12
(2006)
975–1004.
633
[19]
the Future School Buildings ?, in: CIBSE Tech. Symp., Liverpool, UK, 2013.
634 635
S. Steiger, J.K. Roth, L. Østergaard, Hybrid Ventilation – The Best Ventilation Concept in
[20]
M. Gil-Baez, Á. Barrios-Padura, M. Molina-Huelva, R. Chacartegui, A. Barrios-Padura,
636
M. Molina-Huelva, R. Chacartegui, Natural ventilation systems in 21st-century for near
637
zero
638
doi:10.1016/j.energy.2017.05.188.
639
[21]
energy
school
buildings,
Energy.
137
(2017)
1186–1200.
M. Swami, S. Chandra, Procedures for calculating natural ventilation airflow rates in
640
buildings,
641
http://scholar.google.com/scholar?hl=en&btnG=Search&q=intitle:Procedures+for+Calcul
642
ating+Natural+Ventilation+Airflow+Rates+in+Buildings#0%5Cnhttp://scholar.google.co
643
m/scholar?hl=en&btnG=Search&q=intitle:Procedures+for+calculating+natural+ventilatio
644
n+airfl.
645
[22]
ASHRAE
Final
Rep.
FSEC-CR-163-86.
(1987).
D. Cóstola, B. Blocken, J.L.M. Hensen, Overview of pressure coefficient data in building
646
energy simulation and airflow network programs, Build. Environ. 44 (2009) 2027–2036.
647
doi:10.1016/j.buildenv.2009.02.006.
648
[23]
D. Cóstola, B. Blocken, M. Ohba, J.L.M. Hensen, Uncertainty in airflow rate calculations
649
due to the use of surface-averaged pressure coefficients, Energy Build. 42 (2010) 881–
650
888. doi:10.1016/j.enbuild.2009.12.010.
651
[24]
R.T. Muehleisen, S. Patrizi, A new parametric equation for the wind pressure coefficient
652
for
low-rise
buildings,
653
doi:10.1016/j.enbuild.2012.10.051.
Energy
Build.
57
(2013)
245–249.
654
[25]
P. Gandhi, G. Brager, S. Dutton, Mixed Mode Simulation Tools, 2014.
655
[26]
P. Gandhi, G. Brager, S. Dutton, A Comparative Study of Mixed Mode Simulation
656
Methods : Approaches in Research and Practice, Spring Simul. Multi-Conference. (2015)
657
1239–1246.
658
[27]
Z. Zhai, M.H. Johnson, M. Krarti, Assessment of natural and hybrid ventilation models in
659
whole-building
660
doi:10.1016/j.enbuild.2011.06.026.
661
[28]
energy
simulations,
transport
663
doi:10.1007/s12273-016-0279-2. [29]
Build.
43
(2011)
2251–2261.
W.S. Dols, S.J. Emmerich, B.J. Polidoro, Coupling the multizone airflow and contaminant
662
664
Energy
software
CONTAM
with
EnergyPlus
using
co-simulation,
2016.
S. Hussain, P.H. Oosthuizen, Validation of numerical modeling of conditions in an atrium
665
space with a hybrid ventilation system, Build. Environ. 52 (2012) 152–161.
666
doi:10.1016/j.buildenv.2011.12.016.
667
[30]
S. Hussain, P.H. Oosthuizen, Numerical study of buoyancy-driven natural ventilation in a
668
simple three-storey atrium building, Int. J. Sustain. Built Environ. 1 (2012) 141–157.
669
doi:10.1016/j.ijsbe.2013.07.001.
670
[31]
J.M. Horan, D.P. Finn, Sensitivity of air change rates in a naturally ventilated atrium space
671
subject to variations in external wind speed and direction, Energy Build. 40 (2008) 1577–
672
1585. doi:10.1016/j.enbuild.2008.02.013.
673
[32]
J.M. Holford, G.R. Hunt, Fundamental atrium design for natural ventilation, Build.
674 675
Environ. 38 (2003) 409–426. doi:10.1016/S0360-1323(02)00019-7. [33]
L. Moosavi, N. Mahyuddin, N. Ab Ghafar, M. Azzam Ismail, Thermal performance of
676
atria: An overview of natural ventilation effective designs, Renew. Sustain. Energy Rev.
677
34 (2014) 654–670. doi:10.1016/j.rser.2014.02.035.
678
[34]
679 680
J.W. Axley, Application of Natural Ventilation for U. S. Commercial Buildings: Climate Suitability, Design Strategies, & Methods Modeling Studies, 2001.
[35]
K. Hiyama, L. Glicksman, Preliminary design method for naturally ventilated buildings
681
using target air change rate and natural ventilation potential maps in the United States,
682
Energy. 89 (2015) 655–666. doi:10.1016/j.energy.2015.06.026.
683
[36]
Y. Chen, Z. Tong, A. Malkawi, Investigating natural ventilation potentials across the
684
globe: Regional and climatic variations, Build. Environ. 122 (2017) 386–396.
685
doi:10.1016/j.buildenv.2017.06.026.
686
[37]
687 688
doi:10.1080/14733315.2004.11683674. [38]
689 690
P. Heiselberg, Natural Ventilation Design, Int. J. Vent. 2 (2004) 295–312.
CIBSE, CIBSE Applications Manual AM10: Natural ventilation in non-domestic buildings, 2005.
[39]
S. Omrani, V. Garcia-Hansen, B. Capra, R. Drogemuller, Natural ventilation in multi-
691
storey buildings: Design process and review of evaluation tools, Build. Environ. 116
692
(2017) 182–194. doi:10.1016/j.buildenv.2017.02.012.
693
[40]
A. Aflaki, N. Mahyuddin, Z. Al-Cheikh Mahmoud, M.R. Baharum, A review on natural
694
ventilation applications through building façade components and ventilation openings in
695
tropical climates, Energy Build. 101 (2015) 153–162. doi:10.1016/j.enbuild.2015.04.033.
696
[41]
A. Belleri, R. Lollini, S.M. Dutton, Natural ventilation design: An analysis of predicted
697
and
698
doi:10.1016/j.buildenv.2014.06.009.
699
[42]
measured
performance,
Build.
Environ.
81
(2014)
123–138.
M. Mora-Pérez, I. Guillén-Guillamón, P.A. López-Jiménez, Computational analysis of
700
wind interactions for comparing different buildings sites in terms of natural ventilation,
701
Adv. Eng. Softw. 88 (2015) 73–82. doi:10.1016/j.advengsoft.2015.06.003.
702
[43]
J.C. Deblois, D. Ndiaye, CFD-assisted design and optimization of solar chimneys for
703
elementary school classrooms, in: 14th Conf. Int. Build. Perform. Simul. Assoc., 2015: pp.
704
818–825.
705
[44]
706 707
A. Malkawi, B. Wang, Genetic Algorithm Based Building Form Optimization Study for Natural Ventilation Potential, Build. Simul. Conf. (2015) 640–647.
[45]
W. Guo, X. Liu, X. Yuan, Study on Natural Ventilation Design Optimization Based on
708
CFD Simulation
709
doi:10.1016/j.proeng.2015.08.1036.
710
[46]
for
Green
Buildings,
Procedia Eng. 121
(2015) 573–581.
A. Rinaldi, M. Roccotelli, A.M. Mangini, M.P. Fanti, F. Iannone, Natural Ventilation for
711
Passive Cooling by Means of Optimized Control Logics, Procedia Eng. 180 (2017) 841–
712
850. doi:10.1016/j.proeng.2017.04.245.
713
[47]
Z. Wang, L. Wang, Intelligent Control of Ventilation System for Energy-Efficient
714
Buildings With Predictive Model, IEEE Trans. Smart Grid. 4 (2013) 686–693.
715
doi:10.1109/TSG.2012.2229474.
716
[48]
M. Hamdy, A.T. Nguyen, J.L.M. Hensen, A performance comparison of multi-objective
717
optimization algorithms for solving nearly-zero-energy-building design problems, Energy
718
Build. 121 (2016) 57–71. doi:10.1016/j.enbuild.2016.03.035.
719
[49]
720 721
Sci. Rev. 44 (2001) 285–295. doi:10.1080/00038628.2001.9697484. [50]
722 723
W.Y. Hung, W.K. Chow, A review on architectural aspects of atrium buildings, Archit.
R.M.S.F. Almeida, V.P. de Freitas, J.M.P.Q. Delgado, School Buildings Rehabilitation, 2015. doi:10.1007/978-3-319-15359-9.
[51]
P.O. Fanger, Introduction of the olf and the decipol units to quantify air pollution
724
perceived by humans indoors and outdoors, Energy Build. 12 (1988) 1–6.
725
doi:10.1016/0378-7788(88)90051-5.
726
[52]
B. Berg-Munch, G. Clausen, P.O. Fanger, Ventilation requirements for the control of body
727
odor in spaces occupied by women, Environ. Int. 12 (1986) 195–199. doi:10.1016/0160-
728
4120(86)90030-9.
729
[53]
P.O. Fanger, B. Berg-Munch, Ventilation Requirements for the control of body odor, in:
730
Proc. an Eng. Found. Conf. Manag. Atmos. Tightly Enclosed Spaces, American Society of
731
heating Refrigerating and Air Conditioning Engineers, Inc., Atlanta, GA, 1983: pp. 45–60.
732 733
[54]
C. Rasmussen, G.H. Clausen, B. Berg-Munch, P.O. Fanger, The influence of human activity on ventilation requirements for the control of body odor, in: Proc. CLIMA 2000
734 735
World Congr. Heating, Vent. Air-Conditioning, 1985: p. Vol. 4, pp. 357–362. [55]
W.S. Cain, B.P. Leaderer, R. Isseroff, L.G. Berglund, R.J. Huey, E.D. Lipsitt, D. Perlman,
736
Ventilation requirements in buildings-I. Control of occupancy odor and tobacco smoke
737
odor, Atmos. Environ. 17 (1983) 1183–1197. doi:10.1016/0004-6981(83)90341-4.
738
[56]
739 740
A. Persily, L. de Jonge, Carbon dioxide generation rates for building occupants, Indoor Air. 27 (2017) 868–879. doi:10.1111/ina.12383.
[57]
741
W.S. Dols, B.J. Polidoro, CONTAM User Guide and Program Documentation - Version 3.2 (NIST Technical Note 1887), 2015. doi:10.6028/NIST.TN.1887.
742
[58]
USDOE, EnergyPlus Documentation, v8.4.0: Engineering Reference, 2015.
743
[59]
RSMeans, Square Foot Costs with RSMeans DATA 2018, Gordian RSMeans data,
744 745
Rockland, MA, 2018. [60]
ASTM, ASTM E1557-09 Standard Classification for Building Elements and Related
746
Sitework — UNIFORMAT II, ASTM International, West Conshohocken, PA, 2009.
747
doi:10.1520/E1557-09R15.2.
748
[61]
K. Deb, A. Pratap, S. Agarwal, T. Meyarivan, A fast and elitist multiobjective genetic
749
algorithm:
750
doi:10.1109/4235.996017.
751
[62]
NSGA-II,
IEEE
Trans.
Evol.
Comput.
6
(2002)
182–197.
P. Reed, B. Minsker, D.E. Goldberg, Designing a competent simple genetic algorithm for
752
search
and
optimization,
753
doi:10.1029/2000WR900231.
Water
Resour.
Res.
36
(2000)
3757–3761.
754
[63]
P. Reed, B.S. Minsker, D.E. Goldberg, Simplifying multiobjective optimization: An
755
automated design methodology for the nondominated sorted genetic algorithm-II, Water
756
Resour. Res. 39 (2003) 1–6. doi:10.1029/2002WR001483.
757
Model Formulation Objective Functions
Design Variables 1. Classroom layout selection 2. Building orientation 3. Floor height
1. Maximize occupant satisfaction with human bioeffluents /body odor levels (OS)
6. Vents length
1. Design variable limits 2. Construction budget 3. Residual space
4. Ventilation shaft height 5. Atrium width
Constraints
2. Minimize construction cost (CC)
7. Classroom window/wall ratio 8. Atrium window/wall ratio 9. Shaft window/wall ratio 10. Classroom occupancy density
Model Implementation 1. Initialization module 2. Optimization module 3. Objective function module Model Evaluation
OS
CC
Classroom Types
(a) Centralized C
A
B
D
,
,
…
Start/End of Wing
,
-
,
,
…
,
-
Atrium
5 …
,
Wing A (w=1) Wing B (w=2)
Start of Floor
,
-
,
Wing C
,
…
,
Wing D
-
,
,
Wing A Floor 2
Floor 1 (f=1)
(b) Semi-enclosed A
C
,
,
…
,
-
,
,
…
,
-
,
,
…
,
-
,
,
…
D Wing A
Wing C
Atrium
Wing D
Floor 1
(c) Linear
Wing A Floor 2
A ,
,
…
,
-
,
,
…
,
-
,
,
…
B Wing A Atrium
Wing B Floor 1
(d) Attached
Wing A Floor 2 Classroom layout selection
A ,
,
…
Wing A Atrium
Classroom type (c)
,
-
,
,
…
,
Wing A
Floor 1 Floor 2 Example classroom types
Where: f = floor, w = wing, and c = classroom
1
2
3
4
5
Daycare (age <4)
Classroom (age 5-8)
Classroom (age 9+)
Lecture Classroom
Lecture Hall (Fixed seats)
Occupants
20
25
40
65
120
Density (#/100 m2)1
25
25
35
65
150
Sides Ratio(1:x)
1.5
1.5
1.8
1.5
1.8
Description1
1From
…
occupancy categories and density default values in Table 6-1 Standard 62.1 (ASHRAE 2010)
True North
Building orientation (O)
Window to wall ratio of classroom (WWRc)
Window to wall ratio of shaft (WWRs)
Window to wall ratio of atrium (WWRa)
Building direction Wing A
Wing B Shaft height (SH) Vents length (VL)
Floor height (FH)
Atrium width (AW)
(a) CO2 concentration variation over one year in a classroom 3,000 CO2 level [ppm] 2,500 2,000 1,500 1,000 500
(b) CO2 concentration variation in a classroom on March 28th Occupnats
CO2 level [ppm]
1,250 1,000
Dec 31
Nov 05
Oct 08
Sep 10
Aug 13
Jul 16
Jun 18
May 21
Apr 23
Mar 26
Feb 26
Jan 29
Jan 01 1,500
Dec 03
Time [day]
0
30 25
Designer-specified acceptable level of CO2: 1000 ppm
750
20 15
650 ppm
500 Outdoor CO2
10
level: 350 ppm
250 0
5 Simulation timesteps of 15 min (s)
1 hr
0 4 8 12 16 20 24 28 32 36 40 44 48 52 56 60 64 68 72 76 80 84 88 92 96 CO2 level limit
Classroom CO2 level
Occupants
0
1,500
t11,87,45 = 0 s
CO2 level [ppm]
t11,87,43 = 533 s
t11,87,34 = 900 s
Occupnats
30
t11,87,48 = 846 s
1,250
25 1,130 ppm
1,016 ppm
20
1,000 811 ppm
744 ppm
750
15
500
10
250
T = 900 s
5
Simulation timesteps (s) 0 0 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60 61 62 63 64 B F CO2 level limit Classroom CO2 level Occupants Total complying daily time with designer-specified CO2 levels Total non-complying daily time with designer-specified CO2 specified levels ,
=
23,876 ∗ 100 = 85.58% (63 − 33 + 1) ∗ 900
Major group element:
A Substructure
Individual element:
A1030 Slab on grade
Assembly item:
4 in reinforced concrete slab with recycled vapor barrier and granular base
Assembly unit cost:
$ 5.84 / S.F.
Building length (Y):
XB=10 m Y=28 m
AW=6 m XA=13 m Design solution
28 m
Wing A width (XA):
13 m
Atrium width (AW):
6m
Wing B width (XB):
10 m
Building Width (X= XA+AW+XB):
29 m
Slab area (X*Y):
812 m2 8,740.3 S.F.
A1030 Slab on grade cost
$ 51,043.35
Start
Initialization Module Project Input Data (1) (2) (3) (4) (5) (6) (7) (8) (9) (10)
Weather data Classroom data Building data Daily schedule of classroom occupancy Construction cost data Contam simulation tool parameters EnergyPlus simulation program parameters Design variable constraints Budget (Bmax) and residual space (RSmax) constraints NSGAII algorithm parameters
Optimization Module
Objective Function Module Solutions (s = 1)
Generate random solutions (s = 1 to S) for initial population P1 of first generation (g=1)
No
Generate building design Design Variables
First generation (g=1) Yes
Sort and rank all solutions (s=1 to S) of initial population P1 based on Pareto optimal rank and crowding distance Generate child population Cg using tournament selection, recombination and mutation Combine child population Cg and parent population Pg to form a new combined population Ng Sort and rank all solutions (s = 1 to S) of combined population Ng based on Pareto optimal rank and crowding distance
Calculate CC objective function and residual space (RS)
Yes
CC ≤ Bmax RS ≤ RSmax
No
Discard and replace solution
Generate simulation files (PRJ, XML, VEF and IDF files)
Perform Contam-EnergyPlus co-simulation Temperatures Airflows Contam
Keep top S solution to form next generation’s parent population Pg+1 No
Last generation
Calculate OS objective function from co-simulation results
Yes Yes
Next generation (g = g + 1)
Last solution No
End
Next solution (s = s + 1)
100%
Occupant satisfaction with human bioeffluents/body odor levels (OS) [%] Solution (c) CC: $4.06M OS: 90.6%
Solution (a) CC: $5.72M OS: 98.4%
90%
80%
70%
60%
50% Solution (b) CC: $3.57M OS: 54.0%
40% $3.4
$3.6
$3.8
$4.0
Construction cost (CC) [Millions $] $4.2
$4.4
$4.6
Non-optimal dominated solutions
$4.8
$5.0
$5.2
$5.4
$5.6
Optimal non-dominated solutions
$5.8
$6.0
Solution (b) CC: $3.57M OS: 54.0%
Solution (c) CC: $4.06M OS: 90.6%
Solution (a) CC: $5.72M OS: 98.4%
Floor 1 (f=1)
Classrooms (c)
Floor 2 (f=2)
Wing A (w=1)
Wing B (w=2)
1 2 3
4 5 6
7 8 9
10
11 12
3 2 2 − 4 3 3 − 1 2 2 − 5 3 1 Classroom layout selection (Lfw,c):
4 2 1 − 5 3 1 − 2 2 2 − 3 3 3 5 4 1 − 3 3 2 − 3 1 2 2 − 3 2
Solution (a)
Solution (b)
Floor 2 Wing B RS
1
4
5
2
Floor 1 Wing B
Floor 1 Wing A
2 3
3 4
5
5 Floor 1 Wing A
4
3
1
3
2
1 1
3
Floor 1 Wing A
1 3
3
3
Floor 2 Wing B
2
2
Floor 2 Wing B
Floor 2 Wing A
Floor 1 Wing B
Floor 2 Wing A
1
2
3
2
2
2
2
3
3
3
Floor 2 Wing A
2 2
Solution (c)
Floor 1 Wing B
September 4, 2019 Chao-Hsin Lin, Ph.D. Editor Building and Environment Ms. Ref. No.: BAE-D-19-01641 Title: Optimal design of classroom spaces in naturally-ventilated buildings to maximize occupant satisfaction with human bioeffluents/body odor levels Authors: Dario F Acosta-Acosta and Khaled El-Rayes Journal: Journals of Building and Environment
Dear Mr. Chao-Hsin Lin, The highlights of this submitted manuscript include: A novel methodology is developed for measuring and quantifying the impact of the design decisions of naturally-ventilated education buildings on classroom acceptability in terms of human bioeffluents/body odor;
An original multi-objective optimization model is elaborated that is capable of generating optimal trade-offs between two critical design objectives of maximizing occupant satisfaction with human bioeffluents/body odor levels and minimizing building construction cost;
The developed model optimizes ten design variables that represent the design decisions of education buildings that have an impact on these conflicting optimization objectives; and Practical capabilities of the developed model are expected to improve current design practices of naturally-ventilated education buildings and will contribute to maximizing occupant satisfaction with human bioeffluents/body odor levels while minimizing their construction cost. Please let me know if you need any additional information. Best Regards, Dario F Acosta Acosta PhD Candidate, (the corresponding author) Department of Civil and Environmental Engineering University of Illinois at Urbana-Champaign 3112 Newmark Civil Engineering Laboratory Urbana, Illinois, 61801 and affiliated to Universidad Panamericana Campus Guadalajara Tel: +52 (33) 3025-5984 Email:
[email protected] /
[email protected]
Declaration of interests ☒ The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper. ☐The authors declare the following financial interests/personal relationships which may be considered as potential competing interests: