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Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77
www.ijera.com 71 | P a g e
Green Roofs and Green Building Rating Systems
Liaw, Chao-Hsien*, Huang, En-Hao**, Tzai, Hsin-Yuan***
*(Professor, Department of Harbor and River Engineering, National Taiwan Ocean University, Taiwan)
** (Ph.D. Candidate, Department of Harbor and River Engineering, National Taiwan Ocean University,
Taiwan)
***(Ph.D. Student, Department of Harbor and River Engineering, National Taiwan Ocean University, Taiwan)
ABSTRACT
The environmental benefits for green building from the Leadership in Energy and Environment Design (LEED)
and Ecology, Energy, Waste, and Health (EEWH) rating systems have been extensively investigated; however,
the effect of green roofs on the credit-earning mechanisms is relatively unexplored. This study is concerned with
the environmental benefits of green roofs with respect to sustainability, stormwater control, energy savings, and
water resources. We focused on the relationship between green coverage and the credits of the rating systems,
evaluated the credits efficiency, and performed cost analysis. As an example, we used a university building in
Keelung, Northern Taiwan. The findings suggest that with EEWH, the proposed green coverage is 50–75%,
whereas with LEED, the proposed green coverage is 100%. These findings have implications for the application
of green roofs in green building.
Keywords - Green building, green roof, green building rating system, LEED, EEWH
I. INTRODUCTION
Taiwan faces serious urbanization and
overexploitation of land resources because of the
country’s economic development (Kalnay and Cai
2003; Kim et al., 2013). Natural habitats have been
covered with concrete, and urbanization has
negatively affected the urban environment (Booth et
al., 2002; Borselli et al., 2010; Hester et al., 2013).
Green space has been replaced. Green roofs are used
in buildings to promote water conservation (Getter et
al., 2006; Oberndorfer et al., 2007), improve the
environment, regulate the microclimate, and mitigate
the heat island effect (Del Barrio, 1998). Green roofs
have gradually become an important trend in green
buildings. To quantitatively assess the performance
of green buildings, many countries have developed
green building rating systems. Green roofs are quite
important as they play a significant role in site
development (Nektarios et al., 2011), irrigation, flood
control (Mentens et al., 2006; Teemusk et al., 2007),
and mitigate the heat island effect (Oberndorfer,
2007; Takebayashi, 2007).
A “Green Roof” is defined as a roof with plant
growth on the roof surface, which ranges from
spontaneous growth of moss to full-scale garden with
shrubs and trees (Scholz-Barth, 2001). From bottom
to top, the layers of a green roof comprise the water
proofing membrane, water-storage and drain layer,
filter layer, and growing medium and vegetation (Fig.
1). The waterproofing membrane and root-protection
layer are placed at the bottom of the plot to protect
the building from moisture and roots. The water-
storage and drain layer are used to store rainwater in
arid conditions and drain storm
water, respectively. This layer can effectively
decrease the storm water volume and reduce the heat
island effect. The filter layer prevents the washing
out of the growing medium. The growing medium
layer also decreases the stormwater volume and
reduces the heat island effect. The thickness of the
medium depends on structural constraints and the
type of vegetation. The latter should be native or
adapted plants.
Figure 1 Constituent layers of a green roof
In the 20th century, many developing countries
developed green building techniques and established
green building rating systems, such as the UK
Building Research Establishment Environmental
Assessment Method, Australia’s National Australia
Building Environmental Rating System, Japan’s
Comprehensive Assessment for Building
Environmental Efficiency, and the US Leadership in
Energy and Environment Design (LEED). The
latter’s influence is global. The building blocks of the
Taiwan green building rating system are Ecology,
Energy, Waste, and Health (EEWH). This study
discusses and compares the EEWH and LEED rating
systems.
RESEARCH ARTICLE OPEN ACCESS
Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com
ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77
www.ijera.com 72 | P a g e
II. EEWH & LEED
In 1999, Taiwan’s Ministry of the Interior,
Architecture, and Building Research Institute (ABRI)
developed the EEWH green building rating system.
The EEWH system is based on nine assessment
indexes: biodiversity, greenness, water conservation,
energy savings, CO2 emissions reduction, waste
reduction, water resources, indoor environmental
quality, and garbage and sewage improvements.
There are five levels (credits) in EEWH: certified
level (12–26), copper level (26–34), silver level (42–
52), gold level (42–52), and diamond level (≥53); the
total credit score is 100.
In 1995, the U.S. Green Building Council
published LEED. LEED is a system for rating the
design, construction, operation, and maintenance of
green buildings, homes and neighborhoods. There are
six assessments: sustainable sites (SS), water
efficiency (WE), energy and atmosphere (EA),
materials and resources (MR), indoor environmental
quality (IEQ), and innovation in design (ID). There
four levels (credits) in LEED: certified level (40–49),
silver level (50–59), gold level (60–79), and platinum
level (≥80); the sum of credits is 110.
III. Environmental Benefits of Green
Roofs
Regardless of using EEWH or LEED, green
roofs can improve the built environment. Green roofs
are critical for earning credits in rating systems and
are indispensable parts of green buildings. This study
is based on EEWH-BC V8 (ABRI, 2012) and LEED
2009 (USGBC, 2009).
3.1 Green roofs in EEWH
In the nine assessment indexes of EEWH, there
are up to four indexes associated with green roofs:
greenness, water conservation, energy saving, and
water resource.
(1) Greenness
Greenness uses the plants’ photosynthesis
capacity as a part of the evaluation criteria.
According to weather conditions, tree shape, and leaf
area, analysis of the CO2 fixation capacity as green
conversion efficiency standards can be performed.
The weighted criteria and greening credits are
calculated as follows:
  
1.5
/standardstandard-valuecalculatedfixationCO6.81
creditsGreenness
2


Eq. (1)
   arealueixation vafCOplants
valuecalculatedfixationCO
2
2
Eq. (2)
For the CO2 fixation capacity, one can refer to
the EEWH-BC manual. Because the soil layer is thin,
green roofs are often used to grow lawns, vines, low-
growth shrubs, etc. The use of shrubs can increase to
enhance the CO2 fixation capacity.
(2) Water conservation
Water conservation is basically rainwater
catchment capacity; it enhances microbial activity
and improves the environment. Water conservation
depends on the soil layer porosity. Green roofs
control the runoff volume, delay the runoff peak time,
and reduce the risk of urban flooding. The weighted
criteria and water conservation credits are calculated
as follows:
  
1.5
value/standardvaluestandard-valuecalculated0.4
creditsonconservatiWater


Eq. (3)
tdevelopmenbeforeonconservatiwater
tdevelopmenafteronconservatiwater
valuecalculated 
Eq. (4)
The water conservation can be calculated by using
the medium volume and type.
(3) Energy savings
Energy savings is a necessary index of EEWH-
BC. Energy savings include the building shell,
HVAC, and lighting systems. Green roofs improve
the building shell energy performance.
Energy savings should be more than 20% of the
benchmark for current energy efficiency regulations.
Therefore, the key to energy savings is the roof
insulation. The weighted criteria and energy saving
credits are calculated as follows:
  
2.0
/0.80efficiencyenergyshellbuilding-0.08
creditssavingEnergy

 a
Eq. (5)
0.8valuecalculatedenergyshellbuilding
valuestandardenergyshellbuilding
valuecalculatedenergyshellbuilding
efficiencyenergyshellbuilding


Eq. (6)
For the definition of the weighting factor a, the reader
should refer to the EEWH-BC manual.
(4) Water resources
Taiwan has an average annual rainfall of more
than 2600 mm. However, because of increasing
Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com
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industry and business requirements and high
population density, the water amount per person is
only one-sixth of the world’s average. Taiwan is
defined as a water-scarce country by the UN, and
green roof irrigation only compounds the problem of
water scarcity. Therefore, green roofs should make
use of plants that do not require much water and
combine them with automatic and water-saving
irrigation systems. Moreover, green roofs should
harvest rainwater and use graywater for irrigation.
Water resource is one of the indexes of EEWH-BC.
The weighted criteria and water-saving credits are
calculated as follows:
  1.5/2.02.0-indexesresourcewater5.2
creditsresourceWater

Eq. (7)
FEDCBA indexesresourcewater
Eq. (8)
where A is the toilet credit; B is the urinal credit; C is
the public lavatory faucet credit; D is the bath or
shower credit; E is the rainwater or graywater credit;
and F is the air-conditioning credit.
3.2 Green roof in LEED
In LEED, there are up to five sub-indexes
associated with green roofs: 1) sustainable sites: site
development–maximize open space (SSC5.2); 2)
sustainable sites: stormwater design–quantity control
(SSC6.1); 3) sustainable sites: heat island effect–roof
(SSC7.1); 4) water efficiency: water-efficient
landscaping (WEC1); and 5) energy and atmosphere:
optimize energy performance (EAC1).
(1) Sustainable sites: site development–maximize
open space (SSC5.2)
Open space provides habitat for vegetation and
wildlife. Plants that support insects and other
pollinators can help sustain populations higher up the
food chain. Open space also minimizes the urban heat
island effect, increases infiltration, and connects
humans population to the outdoors. If the area is
already developed, the roof area can be green.
To earn one credit, the development footprint should
be minimal, the vegetated open spaces within the
project boundaries should exceed local zoning
requirements by 25%, or the vegetated open space
should equal 20% of the project’s site area. To earn
two credits, the open space must exceed the local
zoning requirements by 50%, or the vegetated open
space must equal 40% of the project’s site area.
(2) Sustainable sites: stormwater design–quantity
control (SSC6.1)
Stormwater is a major source of water pollution.
Roads and parking lots produce stormwater runoff
that contains sediment and other contaminants, such
as atmospheric materials, pesticides, fertilizers,
vehicle fluid, and mechanical equipment waste.
Furthermore, municipal systems that transport and
treat water runoff require significant infrastructure
and maintenance. Green roofs provide effective on-
site management practices and allow stormwater
infiltration, thereby reducing the volume and
intensity of stormwater flows.
To earn credits, the postdevelopment peak discharge
rate and quantity should not exceed the
predevelopment peak discharge rate and quantity for
one- and two-year 24-h storms.
(3) Sustainable sites: heat island effect–roof (SSC7.1)
The use of dark, nonreflective roofing surfaces
contributes to the heat island effect by absorbing the
sun’s warmth. Ambient temperatures in urban areas
are accordingly elevated, thereby increasing cooling
loads, electricity consumption, emissions of
greenhouse gases, and pollution. The heat island
effect is also detrimental to site habitats, and plants
and animals may not thrive in areas affected by it.
One credit is earned for a vegetated roof that covers
at least 50% of the roof area. Two credits are earned
for 100% coverage.
(4) Water efficiency: water-efficient landscaping
(WEC1)
Landscape irrigation practices consume large
quantities of potable water. Therefore, improved
landscaping practices can dramatically reduce and
even eliminate irrigation requirements. Maintaining
or re-establishing native or adapted plants on building
sites fosters self-sustaining landscapes that require
minimal addition of water and attracts native wildlife,
creating a building site that is integrated with the
natural surroundings.
LEED and EEWH aim at water efficiency,
watering frequency reduction, high-efficiency
irrigation, and use of alternative water sources. To
calculate the credits for the percentage reduction in
potable or natural water use, a baseline water-use rate
for the project is established and then the as-designed
water-use rate is calculated. The evapotranspiration is
based on the landscape, species, density, and
microclimate. To earn two credits, the water demand
for landscape irrigation must be reduced by 50%. For
four credits, no potable water should be used.
Nonetheless, if the green area is less than 5% of the
base area no credits are earned.
Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com
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Table 1 Comparison of the EEWH and LEED rating systems
Environme
ntal
Benefits
EEWH
Ecology, Energy, Waste, and Health
(ABRI, 2012) (Taiwan)
LEED
Leadership in Energy and Environment Design
(USGBC, 2009) (U.S.A.)
Sustainable
Site
Index-2
Greenne
ss
Use plant photosynthesis
capacity as evaluation
criterion according to
sunshine, weather
conditions, tree shape, leaf
area, and CO2 fixation
capacity.
SSC5.2
Development–
Maximize Open
Space
Planting native and adaptive
plants. Use green coverage
area in the evaluation
criteria.
SSC7.2
Heat Island
Effect–Roof
Improve the heat island
effect. Use green coverage
area in the evaluation
criteria.
Stormwater
Control
Index-3
Water
Conserv
ation
Use the water conservation
formula to calculate the
retained runoff volume of
green roof.
SSC6.1
Stormwater
Design–
Quantity
Control
Use the water conservation
formula to calculate the
retained runoff volume of
the green roof.
Energy
Saving
Index-4
Energy
Saving
Energy savings include the
building shell, HVAC, and
lighting systems. Green
roofs improve the building
shell. The energy
performance is part of the
evaluation criteria.
EAC1
Optimize
Energy
Performance
Simulate the whole building
energy using the ASHRAE
90.1 standard. Use the
Green Roof Energy
Calculator to calculate the
energy cost savings.
Water
Resource
Index-5
Water
Resourc
e
The water resources index
formula is based on whether
rainwater or graywater is
used.
WEC1
Water-Efficient
Landscaping
Use alternative water
sources and native and
adaptive plants. Use the
water reduction in the
landscape irrigation in the
evaluation criteria.
(5) Energy and atmosphere: optimize energy
performance (EAC1)
LEED energy efficiency simulations of the
whole building and cost-saving calculations are based
on the ASHRAE 90.1 standard. LEED is different
from EEWH in that regard because it targets the
building shell energy consumption. Green roofs in
LEED can use the green roof energy calculator
(Sailor, 2008) to calculate and compare the annual
energy performance between green roof and
nongreen roof buildings.
3.3 Rating system comparison
The EEWH and LEED rating systems are
compared on the basis of the four categories of
environmental benefits: sustainable site, stormwater
control, energy savings, and water resources. The
rating system comparison is listed in Table 1.
In the sustainable site category, the evaluation
criteria of LEED and EEWH are completely different.
LEED uses the green coverage area percentage,
whereas EEWH uses the plant photosynthesis and the
CO2 fixation capacity. In the energy saving category,
LEED simulates the energy of the whole building by
using the green roof energy calculator, whereas
EEWH use the energy performance formula.
IV. Case study
A university building in Keelung, Northern
Taiwan is used as the case study. The efficiency of
the credit concept and cost are assessed.
Figure 2 Location of the building
4.1 Background
National Taiwan Ocean University (NTOU)
evaluated the feasibility of increasing the number of
green roofs on campus to increase green space and to
included it in the Taiwan Sustainable Campus
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Program [23]. Therefore, a section of the Harbor and
River Engineering Department building was
evaluated (Fig. 2). This is a single five-story building.
The catchment area and green roof is 564 m2, the
medium is 30 cm thick, and the plant used is
Eremochloa ophiuroides (centipede grass). A
rainwater harvesting system was used for irrigation.
Table 1 lists the major meteorological data used in
this study. The mean annual rainfall in the Keelung
area is 3659 mm. During the past 20 years (1993–
2012), the northeast monsoon in the fall and winter is
responsible for the rainy seasons in Keelung, with
considerably lower rainfall present in the summer.
Fig. 4 shows that the irrigation requirements are high
from July to September on account of strong ET
effects of the vegetation during the summer.
Table 2 Hydrological and Meteorological Data
Figure 3 Monthly average rainfall and ET
4.2 Rating systems credits
Using green coverage percentages of 0%, 25%,
50%, 75%, and 100% the EEWH and LEED rating
systems are evaluated.
(1) EEWH credits
The EEWH credits are for greenness, water
conservation, energy savings, and water resources, as
shown on Fig. 4.
For the greenness index, if the green coverage is
0%, no credit is earned; for 25% green coverage, no
credit is earned; for 50% green coverage, one credit
is earned; for 75% green coverage, two credits; and
for 100% green coverage, two credits. For the water
conservation index, if the green coverage is 0%, no
credit is earned; for 25% green coverage, no credit;
for 50% green coverage, one credit; for 75% green
coverage, two credits; and for 100% green coverage,
two credits. For the energy saving index, if the green
coverage is 0%, no credit is earned; for 25% green
coverage, no credit; for 50% green coverage, no
credit; for 75% green coverage, one credit; for 100%
green coverage, one credit. For the water resource
index, if the green coverage is 0%, no credit is earned;
for 25% green coverage, no credit; for 50% green
coverage, one credit; for green 75% coverage, two
credits; for 100% green coverage, two credits.
Using EEWH, if the green coverage is 0%, the total
credit is zero; if the green coverage is 25%, the total
credits are four; if the green coverage is 50%, the
total credits are six; if the green coverage is 75%, the
total credits are nine; and if the green coverage is
100%, the total credits are still nine.
(2) LEED credits
LEED assigns credits for site development–maximize
open space, stormwater design–quantity
Figure 4 EEWH credits for the case study building
control, heat island effect–roof, water-efficient
landscaping, and for optimizing the energy
performance, as shown in Fig. 5.
For the site development–maximize open space
credit, if the green coverage is 0%, no credit is earned;
for 25% green coverage, no credit; for 50% green
coverage, one credit; for 75% green coverage, one
credit; and for 100% green coverage, two credits. For
the stormwater design–quantity control credit, if the
green coverage is 0%, no credit is given; for 25%
green coverage, one credit; for 50% green coverage,
one credit; for 75% green coverage, one credit; and
for 100% green coverage, one credit. For the heat
island effect–roof credit, if the green coverage is 0%,
LEED assigns no credit; for green coverage 25%, no
credit; for 50% green coverage, one credit; for 75%
green coverage, two credits; for green coverage
100%, two credits. For the water-efficient
landscaping credit, if the green coverage is 0%,
LEED assigns no credit; for 25% green coverage,
four credits; for 50% green coverage, four credits; for
75% green coverage, four credits; and for 100%
Average annual data of the Keelung weather station
(1993–2012)
Rainfall 3595 mm
Sunshine 139.7 days
Temperature 22.4 °C
Atmospheric Pressure 1011.2 hPa
Wind Speed 2.8 m/s
Humidity 78.9 %
0
50
100
150
200
250
300
1 2 3 4 5 6 7 8 9 10 11 12
Month
ET(mm)
0
100
200
300
400
500
600
700
Rainfall(mm)
ET(mm) Rainfall(mm)
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green coverage, four credits. For the optimize energy
performance credit, if the green coverage is 0%,
LEEDS assigns no credit; for 25% green coverage,
no credit; for 50% green coverage, no credit; for 75%
green coverage, no credit; and for 100% green
coverage, one credit.
Using LEED, if the green coverage is 0%, the
total credit is zero; if the green coverage is 25%, the
total credits are five; if the green coverage is 50%,
the total credits are six; if the green coverage is 75%,
the total credits are seven; and if green coverage is
100%, the total credits are still eleven.
4.3 Credits efficiency
The credits based on the two systems and the
Figure 5 LEED credits for the case study building
analysis of the efficiency of the credits with respect
to green coverage are discussed and shown in Fig. 6.
4.3 Credits efficiency
The credits based on the two systems and the
analysis of the efficiency of the credits with respect
to green coverage are discussed and shown in Fig. 6.
Using EEWH, if the green coverage is 0%, the credits
efficiency is 0%; if the green coverage is 25%, the
credits efficiency is 4.0%; if the green coverage is
50%, the credits efficiency is 6.0%; if the green
coverage is 75%, the credits efficiency is 9.0%; and if
the green coverage is 100%, the credits efficiency is
9.0%. Using LEED, if the green coverage is 0%, the
credits efficiency is 0%; for 25% green coverage, the
credits efficiency is 4.5%; for 50% green coverage,
the credits efficiency is 5.5%; for 75% green
coverage, the credits efficiency is 6.4%; for 100%
green coverage, the credits efficiency is 9.1%.
When the green coverage is 25% to 50%, the credits
are nearly equal; for 75% green coverage, the EEWH
credits are greater than LEED by 3.6%. The EEWH
assigns more credits for 75% green coverage,
whereas there no significant differences (0.1%) at
100% green coverage between LEED and EEWH.
4.4 Cost analysis
In this study, we evaluate the green roof
environmental benefits based on LEED and EEWH.
The purpose is to investigate what it costs to earn the
credits of each rating system. In Taiwan, the
established cost for green roofs is $USD 66.67/m2
(Chen, 2013). To establish the rainwater harvesting
system cost, we have to consider the green coverage
percentage. If the green coverage is 25%, the cost is
$USD 1667; for 50% green coverage, the cost are
$USD 2333; for 75% green coverage, the cost is
$USD 3000; and if the green coverage is 100%, the
cost is $USD 3333. We look at the cost per credit
with respect to green coverage.
Using EEWH, if the green coverage is 0%, the
cost is $USD 0/per point; for 25% green coverage,
the cost is $USD 2758/per point; for 50% green
coverage, the cost is $USD 3511/per point; for 75%
green coverage, the cost is $USD 3456/per point; and
for 100% green coverage, the cost is $USD 4533/per
point. Using LEED, if green coverage is 0%, the cost
is $USD 0/per point; for 25% green coverage, the
cost is $USD 2427/per point; for 50% green coverage,
the cost is $USD 3862/per point; for
Figure 6 EEWH & LEED credits efficiency
Figure 7 Cost analysis of EEWH & LEED
75% green coverage, the cost is $USD 4887/per point;
and if the green coverage is 100%, the cost is $USD
4488/per point.
Because there are no more credits for ≥75%
green coverage when using EEWH, the segment cost
increases significantly. Because there are
significantly increased credits at 100% green
coverage for LEED, the segment cost markedly
decrease. On the basis of the earned credits and cost,
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EEWH is recommended for 50–75% green coverage
and LEED is recommended for 100% green coverage.
V. Discussion and conclusions
This is a preliminary study of the environmental
benefits of green roofs according to green building
rating systems. A major finding is the difference in
credit efficiency between EEWH and LEED. The
results indicate that the rating system and green
coverage should be considered in the cost analysis.
As case study, we considered a NTOU building in
Keelung, Northern Taiwan. Green roofs with 50–
75% green coverage are proposed for EEWH and
100% green coverage for LEED. This type of
analysis could offer specific advice for green building
practices and systematize the credit-earning
mechanisms.
Despite the EEWH and LEED rating systems
advantages, they do have limitations. First, the
EEWH credits are limited for ≥75% green coverage
and the LEED energy savings are indirectly
calculated by auxiliary models. Particularly
challenging is the green roof management for
maintaining the environmental benefits. It is
important to discuss whether there are environmental
benefits of the two systems that are not considered.
This study has demonstrated that credit efficiency is
critical. However, whether this also applies to other
rating systems cannot be determined from the results
of this study. Further research is therefore required.
Finally, this study has clarified several issues or has
at least paved the way for new research projects that
will add to the study of green building rating system.
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Coffman, R. R., Doshi, H., Dunnett, N., et
al. (2007). Green roofs as urban ecosystems:
ecological structures, functions, and
services. BioScience, 57(10), 823-833.
[13] Scholz-Barth, K. (2001). Green roofs:
Stormwater management from the top down.
Environmental Design & Construction, 4,
63-70.
[14] Sailor, D. (2008). A green roof model for
building energy simulation programs.
Energy and Buildings, 40(8), 1466-1478.
[15] Takebayashi, H., & Moriyama, M. (2007).
Surface heat budget on green roof and high
reflection roof for mitigation of urban heat
island. Building and Environment, 42(8),
2971-2979.
[16] Teemusk, A., & Mander, l. (2007).
Rainwater runoff quantity and quality
performance from a greenroof: The effects
of short-term events. Ecological
Engineering, 30(3), 271-277.
[17] USGBC, US Green Building Council.
(2009). LEED Reference Guide for Green
Building Design and Construction.
Washington, DC: US Green Building
Council.

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Green Roofs and Green Building Rating Systems

  • 1. Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77 www.ijera.com 71 | P a g e Green Roofs and Green Building Rating Systems Liaw, Chao-Hsien*, Huang, En-Hao**, Tzai, Hsin-Yuan*** *(Professor, Department of Harbor and River Engineering, National Taiwan Ocean University, Taiwan) ** (Ph.D. Candidate, Department of Harbor and River Engineering, National Taiwan Ocean University, Taiwan) ***(Ph.D. Student, Department of Harbor and River Engineering, National Taiwan Ocean University, Taiwan) ABSTRACT The environmental benefits for green building from the Leadership in Energy and Environment Design (LEED) and Ecology, Energy, Waste, and Health (EEWH) rating systems have been extensively investigated; however, the effect of green roofs on the credit-earning mechanisms is relatively unexplored. This study is concerned with the environmental benefits of green roofs with respect to sustainability, stormwater control, energy savings, and water resources. We focused on the relationship between green coverage and the credits of the rating systems, evaluated the credits efficiency, and performed cost analysis. As an example, we used a university building in Keelung, Northern Taiwan. The findings suggest that with EEWH, the proposed green coverage is 50–75%, whereas with LEED, the proposed green coverage is 100%. These findings have implications for the application of green roofs in green building. Keywords - Green building, green roof, green building rating system, LEED, EEWH I. INTRODUCTION Taiwan faces serious urbanization and overexploitation of land resources because of the country’s economic development (Kalnay and Cai 2003; Kim et al., 2013). Natural habitats have been covered with concrete, and urbanization has negatively affected the urban environment (Booth et al., 2002; Borselli et al., 2010; Hester et al., 2013). Green space has been replaced. Green roofs are used in buildings to promote water conservation (Getter et al., 2006; Oberndorfer et al., 2007), improve the environment, regulate the microclimate, and mitigate the heat island effect (Del Barrio, 1998). Green roofs have gradually become an important trend in green buildings. To quantitatively assess the performance of green buildings, many countries have developed green building rating systems. Green roofs are quite important as they play a significant role in site development (Nektarios et al., 2011), irrigation, flood control (Mentens et al., 2006; Teemusk et al., 2007), and mitigate the heat island effect (Oberndorfer, 2007; Takebayashi, 2007). A “Green Roof” is defined as a roof with plant growth on the roof surface, which ranges from spontaneous growth of moss to full-scale garden with shrubs and trees (Scholz-Barth, 2001). From bottom to top, the layers of a green roof comprise the water proofing membrane, water-storage and drain layer, filter layer, and growing medium and vegetation (Fig. 1). The waterproofing membrane and root-protection layer are placed at the bottom of the plot to protect the building from moisture and roots. The water- storage and drain layer are used to store rainwater in arid conditions and drain storm water, respectively. This layer can effectively decrease the storm water volume and reduce the heat island effect. The filter layer prevents the washing out of the growing medium. The growing medium layer also decreases the stormwater volume and reduces the heat island effect. The thickness of the medium depends on structural constraints and the type of vegetation. The latter should be native or adapted plants. Figure 1 Constituent layers of a green roof In the 20th century, many developing countries developed green building techniques and established green building rating systems, such as the UK Building Research Establishment Environmental Assessment Method, Australia’s National Australia Building Environmental Rating System, Japan’s Comprehensive Assessment for Building Environmental Efficiency, and the US Leadership in Energy and Environment Design (LEED). The latter’s influence is global. The building blocks of the Taiwan green building rating system are Ecology, Energy, Waste, and Health (EEWH). This study discusses and compares the EEWH and LEED rating systems. RESEARCH ARTICLE OPEN ACCESS
  • 2. Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77 www.ijera.com 72 | P a g e II. EEWH & LEED In 1999, Taiwan’s Ministry of the Interior, Architecture, and Building Research Institute (ABRI) developed the EEWH green building rating system. The EEWH system is based on nine assessment indexes: biodiversity, greenness, water conservation, energy savings, CO2 emissions reduction, waste reduction, water resources, indoor environmental quality, and garbage and sewage improvements. There are five levels (credits) in EEWH: certified level (12–26), copper level (26–34), silver level (42– 52), gold level (42–52), and diamond level (≥53); the total credit score is 100. In 1995, the U.S. Green Building Council published LEED. LEED is a system for rating the design, construction, operation, and maintenance of green buildings, homes and neighborhoods. There are six assessments: sustainable sites (SS), water efficiency (WE), energy and atmosphere (EA), materials and resources (MR), indoor environmental quality (IEQ), and innovation in design (ID). There four levels (credits) in LEED: certified level (40–49), silver level (50–59), gold level (60–79), and platinum level (≥80); the sum of credits is 110. III. Environmental Benefits of Green Roofs Regardless of using EEWH or LEED, green roofs can improve the built environment. Green roofs are critical for earning credits in rating systems and are indispensable parts of green buildings. This study is based on EEWH-BC V8 (ABRI, 2012) and LEED 2009 (USGBC, 2009). 3.1 Green roofs in EEWH In the nine assessment indexes of EEWH, there are up to four indexes associated with green roofs: greenness, water conservation, energy saving, and water resource. (1) Greenness Greenness uses the plants’ photosynthesis capacity as a part of the evaluation criteria. According to weather conditions, tree shape, and leaf area, analysis of the CO2 fixation capacity as green conversion efficiency standards can be performed. The weighted criteria and greening credits are calculated as follows:    1.5 /standardstandard-valuecalculatedfixationCO6.81 creditsGreenness 2   Eq. (1)    arealueixation vafCOplants valuecalculatedfixationCO 2 2 Eq. (2) For the CO2 fixation capacity, one can refer to the EEWH-BC manual. Because the soil layer is thin, green roofs are often used to grow lawns, vines, low- growth shrubs, etc. The use of shrubs can increase to enhance the CO2 fixation capacity. (2) Water conservation Water conservation is basically rainwater catchment capacity; it enhances microbial activity and improves the environment. Water conservation depends on the soil layer porosity. Green roofs control the runoff volume, delay the runoff peak time, and reduce the risk of urban flooding. The weighted criteria and water conservation credits are calculated as follows:    1.5 value/standardvaluestandard-valuecalculated0.4 creditsonconservatiWater   Eq. (3) tdevelopmenbeforeonconservatiwater tdevelopmenafteronconservatiwater valuecalculated  Eq. (4) The water conservation can be calculated by using the medium volume and type. (3) Energy savings Energy savings is a necessary index of EEWH- BC. Energy savings include the building shell, HVAC, and lighting systems. Green roofs improve the building shell energy performance. Energy savings should be more than 20% of the benchmark for current energy efficiency regulations. Therefore, the key to energy savings is the roof insulation. The weighted criteria and energy saving credits are calculated as follows:    2.0 /0.80efficiencyenergyshellbuilding-0.08 creditssavingEnergy   a Eq. (5) 0.8valuecalculatedenergyshellbuilding valuestandardenergyshellbuilding valuecalculatedenergyshellbuilding efficiencyenergyshellbuilding   Eq. (6) For the definition of the weighting factor a, the reader should refer to the EEWH-BC manual. (4) Water resources Taiwan has an average annual rainfall of more than 2600 mm. However, because of increasing
  • 3. Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77 www.ijera.com 73 | P a g e industry and business requirements and high population density, the water amount per person is only one-sixth of the world’s average. Taiwan is defined as a water-scarce country by the UN, and green roof irrigation only compounds the problem of water scarcity. Therefore, green roofs should make use of plants that do not require much water and combine them with automatic and water-saving irrigation systems. Moreover, green roofs should harvest rainwater and use graywater for irrigation. Water resource is one of the indexes of EEWH-BC. The weighted criteria and water-saving credits are calculated as follows:   1.5/2.02.0-indexesresourcewater5.2 creditsresourceWater  Eq. (7) FEDCBA indexesresourcewater Eq. (8) where A is the toilet credit; B is the urinal credit; C is the public lavatory faucet credit; D is the bath or shower credit; E is the rainwater or graywater credit; and F is the air-conditioning credit. 3.2 Green roof in LEED In LEED, there are up to five sub-indexes associated with green roofs: 1) sustainable sites: site development–maximize open space (SSC5.2); 2) sustainable sites: stormwater design–quantity control (SSC6.1); 3) sustainable sites: heat island effect–roof (SSC7.1); 4) water efficiency: water-efficient landscaping (WEC1); and 5) energy and atmosphere: optimize energy performance (EAC1). (1) Sustainable sites: site development–maximize open space (SSC5.2) Open space provides habitat for vegetation and wildlife. Plants that support insects and other pollinators can help sustain populations higher up the food chain. Open space also minimizes the urban heat island effect, increases infiltration, and connects humans population to the outdoors. If the area is already developed, the roof area can be green. To earn one credit, the development footprint should be minimal, the vegetated open spaces within the project boundaries should exceed local zoning requirements by 25%, or the vegetated open space should equal 20% of the project’s site area. To earn two credits, the open space must exceed the local zoning requirements by 50%, or the vegetated open space must equal 40% of the project’s site area. (2) Sustainable sites: stormwater design–quantity control (SSC6.1) Stormwater is a major source of water pollution. Roads and parking lots produce stormwater runoff that contains sediment and other contaminants, such as atmospheric materials, pesticides, fertilizers, vehicle fluid, and mechanical equipment waste. Furthermore, municipal systems that transport and treat water runoff require significant infrastructure and maintenance. Green roofs provide effective on- site management practices and allow stormwater infiltration, thereby reducing the volume and intensity of stormwater flows. To earn credits, the postdevelopment peak discharge rate and quantity should not exceed the predevelopment peak discharge rate and quantity for one- and two-year 24-h storms. (3) Sustainable sites: heat island effect–roof (SSC7.1) The use of dark, nonreflective roofing surfaces contributes to the heat island effect by absorbing the sun’s warmth. Ambient temperatures in urban areas are accordingly elevated, thereby increasing cooling loads, electricity consumption, emissions of greenhouse gases, and pollution. The heat island effect is also detrimental to site habitats, and plants and animals may not thrive in areas affected by it. One credit is earned for a vegetated roof that covers at least 50% of the roof area. Two credits are earned for 100% coverage. (4) Water efficiency: water-efficient landscaping (WEC1) Landscape irrigation practices consume large quantities of potable water. Therefore, improved landscaping practices can dramatically reduce and even eliminate irrigation requirements. Maintaining or re-establishing native or adapted plants on building sites fosters self-sustaining landscapes that require minimal addition of water and attracts native wildlife, creating a building site that is integrated with the natural surroundings. LEED and EEWH aim at water efficiency, watering frequency reduction, high-efficiency irrigation, and use of alternative water sources. To calculate the credits for the percentage reduction in potable or natural water use, a baseline water-use rate for the project is established and then the as-designed water-use rate is calculated. The evapotranspiration is based on the landscape, species, density, and microclimate. To earn two credits, the water demand for landscape irrigation must be reduced by 50%. For four credits, no potable water should be used. Nonetheless, if the green area is less than 5% of the base area no credits are earned.
  • 4. Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77 www.ijera.com 74 | P a g e Table 1 Comparison of the EEWH and LEED rating systems Environme ntal Benefits EEWH Ecology, Energy, Waste, and Health (ABRI, 2012) (Taiwan) LEED Leadership in Energy and Environment Design (USGBC, 2009) (U.S.A.) Sustainable Site Index-2 Greenne ss Use plant photosynthesis capacity as evaluation criterion according to sunshine, weather conditions, tree shape, leaf area, and CO2 fixation capacity. SSC5.2 Development– Maximize Open Space Planting native and adaptive plants. Use green coverage area in the evaluation criteria. SSC7.2 Heat Island Effect–Roof Improve the heat island effect. Use green coverage area in the evaluation criteria. Stormwater Control Index-3 Water Conserv ation Use the water conservation formula to calculate the retained runoff volume of green roof. SSC6.1 Stormwater Design– Quantity Control Use the water conservation formula to calculate the retained runoff volume of the green roof. Energy Saving Index-4 Energy Saving Energy savings include the building shell, HVAC, and lighting systems. Green roofs improve the building shell. The energy performance is part of the evaluation criteria. EAC1 Optimize Energy Performance Simulate the whole building energy using the ASHRAE 90.1 standard. Use the Green Roof Energy Calculator to calculate the energy cost savings. Water Resource Index-5 Water Resourc e The water resources index formula is based on whether rainwater or graywater is used. WEC1 Water-Efficient Landscaping Use alternative water sources and native and adaptive plants. Use the water reduction in the landscape irrigation in the evaluation criteria. (5) Energy and atmosphere: optimize energy performance (EAC1) LEED energy efficiency simulations of the whole building and cost-saving calculations are based on the ASHRAE 90.1 standard. LEED is different from EEWH in that regard because it targets the building shell energy consumption. Green roofs in LEED can use the green roof energy calculator (Sailor, 2008) to calculate and compare the annual energy performance between green roof and nongreen roof buildings. 3.3 Rating system comparison The EEWH and LEED rating systems are compared on the basis of the four categories of environmental benefits: sustainable site, stormwater control, energy savings, and water resources. The rating system comparison is listed in Table 1. In the sustainable site category, the evaluation criteria of LEED and EEWH are completely different. LEED uses the green coverage area percentage, whereas EEWH uses the plant photosynthesis and the CO2 fixation capacity. In the energy saving category, LEED simulates the energy of the whole building by using the green roof energy calculator, whereas EEWH use the energy performance formula. IV. Case study A university building in Keelung, Northern Taiwan is used as the case study. The efficiency of the credit concept and cost are assessed. Figure 2 Location of the building 4.1 Background National Taiwan Ocean University (NTOU) evaluated the feasibility of increasing the number of green roofs on campus to increase green space and to included it in the Taiwan Sustainable Campus
  • 5. Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77 www.ijera.com 75 | P a g e Program [23]. Therefore, a section of the Harbor and River Engineering Department building was evaluated (Fig. 2). This is a single five-story building. The catchment area and green roof is 564 m2, the medium is 30 cm thick, and the plant used is Eremochloa ophiuroides (centipede grass). A rainwater harvesting system was used for irrigation. Table 1 lists the major meteorological data used in this study. The mean annual rainfall in the Keelung area is 3659 mm. During the past 20 years (1993– 2012), the northeast monsoon in the fall and winter is responsible for the rainy seasons in Keelung, with considerably lower rainfall present in the summer. Fig. 4 shows that the irrigation requirements are high from July to September on account of strong ET effects of the vegetation during the summer. Table 2 Hydrological and Meteorological Data Figure 3 Monthly average rainfall and ET 4.2 Rating systems credits Using green coverage percentages of 0%, 25%, 50%, 75%, and 100% the EEWH and LEED rating systems are evaluated. (1) EEWH credits The EEWH credits are for greenness, water conservation, energy savings, and water resources, as shown on Fig. 4. For the greenness index, if the green coverage is 0%, no credit is earned; for 25% green coverage, no credit is earned; for 50% green coverage, one credit is earned; for 75% green coverage, two credits; and for 100% green coverage, two credits. For the water conservation index, if the green coverage is 0%, no credit is earned; for 25% green coverage, no credit; for 50% green coverage, one credit; for 75% green coverage, two credits; and for 100% green coverage, two credits. For the energy saving index, if the green coverage is 0%, no credit is earned; for 25% green coverage, no credit; for 50% green coverage, no credit; for 75% green coverage, one credit; for 100% green coverage, one credit. For the water resource index, if the green coverage is 0%, no credit is earned; for 25% green coverage, no credit; for 50% green coverage, one credit; for green 75% coverage, two credits; for 100% green coverage, two credits. Using EEWH, if the green coverage is 0%, the total credit is zero; if the green coverage is 25%, the total credits are four; if the green coverage is 50%, the total credits are six; if the green coverage is 75%, the total credits are nine; and if the green coverage is 100%, the total credits are still nine. (2) LEED credits LEED assigns credits for site development–maximize open space, stormwater design–quantity Figure 4 EEWH credits for the case study building control, heat island effect–roof, water-efficient landscaping, and for optimizing the energy performance, as shown in Fig. 5. For the site development–maximize open space credit, if the green coverage is 0%, no credit is earned; for 25% green coverage, no credit; for 50% green coverage, one credit; for 75% green coverage, one credit; and for 100% green coverage, two credits. For the stormwater design–quantity control credit, if the green coverage is 0%, no credit is given; for 25% green coverage, one credit; for 50% green coverage, one credit; for 75% green coverage, one credit; and for 100% green coverage, one credit. For the heat island effect–roof credit, if the green coverage is 0%, LEED assigns no credit; for green coverage 25%, no credit; for 50% green coverage, one credit; for 75% green coverage, two credits; for green coverage 100%, two credits. For the water-efficient landscaping credit, if the green coverage is 0%, LEED assigns no credit; for 25% green coverage, four credits; for 50% green coverage, four credits; for 75% green coverage, four credits; and for 100% Average annual data of the Keelung weather station (1993–2012) Rainfall 3595 mm Sunshine 139.7 days Temperature 22.4 °C Atmospheric Pressure 1011.2 hPa Wind Speed 2.8 m/s Humidity 78.9 % 0 50 100 150 200 250 300 1 2 3 4 5 6 7 8 9 10 11 12 Month ET(mm) 0 100 200 300 400 500 600 700 Rainfall(mm) ET(mm) Rainfall(mm)
  • 6. Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77 www.ijera.com 76 | P a g e green coverage, four credits. For the optimize energy performance credit, if the green coverage is 0%, LEEDS assigns no credit; for 25% green coverage, no credit; for 50% green coverage, no credit; for 75% green coverage, no credit; and for 100% green coverage, one credit. Using LEED, if the green coverage is 0%, the total credit is zero; if the green coverage is 25%, the total credits are five; if the green coverage is 50%, the total credits are six; if the green coverage is 75%, the total credits are seven; and if green coverage is 100%, the total credits are still eleven. 4.3 Credits efficiency The credits based on the two systems and the Figure 5 LEED credits for the case study building analysis of the efficiency of the credits with respect to green coverage are discussed and shown in Fig. 6. 4.3 Credits efficiency The credits based on the two systems and the analysis of the efficiency of the credits with respect to green coverage are discussed and shown in Fig. 6. Using EEWH, if the green coverage is 0%, the credits efficiency is 0%; if the green coverage is 25%, the credits efficiency is 4.0%; if the green coverage is 50%, the credits efficiency is 6.0%; if the green coverage is 75%, the credits efficiency is 9.0%; and if the green coverage is 100%, the credits efficiency is 9.0%. Using LEED, if the green coverage is 0%, the credits efficiency is 0%; for 25% green coverage, the credits efficiency is 4.5%; for 50% green coverage, the credits efficiency is 5.5%; for 75% green coverage, the credits efficiency is 6.4%; for 100% green coverage, the credits efficiency is 9.1%. When the green coverage is 25% to 50%, the credits are nearly equal; for 75% green coverage, the EEWH credits are greater than LEED by 3.6%. The EEWH assigns more credits for 75% green coverage, whereas there no significant differences (0.1%) at 100% green coverage between LEED and EEWH. 4.4 Cost analysis In this study, we evaluate the green roof environmental benefits based on LEED and EEWH. The purpose is to investigate what it costs to earn the credits of each rating system. In Taiwan, the established cost for green roofs is $USD 66.67/m2 (Chen, 2013). To establish the rainwater harvesting system cost, we have to consider the green coverage percentage. If the green coverage is 25%, the cost is $USD 1667; for 50% green coverage, the cost are $USD 2333; for 75% green coverage, the cost is $USD 3000; and if the green coverage is 100%, the cost is $USD 3333. We look at the cost per credit with respect to green coverage. Using EEWH, if the green coverage is 0%, the cost is $USD 0/per point; for 25% green coverage, the cost is $USD 2758/per point; for 50% green coverage, the cost is $USD 3511/per point; for 75% green coverage, the cost is $USD 3456/per point; and for 100% green coverage, the cost is $USD 4533/per point. Using LEED, if green coverage is 0%, the cost is $USD 0/per point; for 25% green coverage, the cost is $USD 2427/per point; for 50% green coverage, the cost is $USD 3862/per point; for Figure 6 EEWH & LEED credits efficiency Figure 7 Cost analysis of EEWH & LEED 75% green coverage, the cost is $USD 4887/per point; and if the green coverage is 100%, the cost is $USD 4488/per point. Because there are no more credits for ≥75% green coverage when using EEWH, the segment cost increases significantly. Because there are significantly increased credits at 100% green coverage for LEED, the segment cost markedly decrease. On the basis of the earned credits and cost,
  • 7. Liaw, Chao-Hsien et al Int. Journal of Engineering Research and Applications www.ijera.com ISSN : 2248-9622, Vol. 5, Issue 1( Part 2), January 2015, pp.71-77 www.ijera.com 77 | P a g e EEWH is recommended for 50–75% green coverage and LEED is recommended for 100% green coverage. V. Discussion and conclusions This is a preliminary study of the environmental benefits of green roofs according to green building rating systems. A major finding is the difference in credit efficiency between EEWH and LEED. The results indicate that the rating system and green coverage should be considered in the cost analysis. As case study, we considered a NTOU building in Keelung, Northern Taiwan. Green roofs with 50– 75% green coverage are proposed for EEWH and 100% green coverage for LEED. This type of analysis could offer specific advice for green building practices and systematize the credit-earning mechanisms. Despite the EEWH and LEED rating systems advantages, they do have limitations. First, the EEWH credits are limited for ≥75% green coverage and the LEED energy savings are indirectly calculated by auxiliary models. Particularly challenging is the green roof management for maintaining the environmental benefits. It is important to discuss whether there are environmental benefits of the two systems that are not considered. This study has demonstrated that credit efficiency is critical. However, whether this also applies to other rating systems cannot be determined from the results of this study. Further research is therefore required. Finally, this study has clarified several issues or has at least paved the way for new research projects that will add to the study of green building rating system. REFERENCES [1] ABRI, Architecture and Building Research Institute. (2012). EEWH-BC: Ministry of the Interior, Taiwan(in Chinese). [2] Barrio, E. P. D. (1998). Analysis of the green roofs cooling potential in buildings. Energy and Buildings, 27(2), 179-193. [3] Booth, D. B., Hartley, D., & Jackson, R. (2002). FOREST COVER, IMPERVIOUS?URFACE AREA, AND THE MITIGATION OF STORMWATER IMPACTS1. JAWRA Journal of the American Water Resources Association, 38(3), 835-845. [4] Borselli, L., & Torri, D. (2010). Soil roughness, slope and surface storage relationship for impervious areas. Journal of Hydrology, 393(3), 389-400. [5] Chen, C. Y. (2013). Construction Budgeting tips - real case costs analysis from tender to contract. Taipei: CHAN'S ARCH- PUBLISHING CO., LTD. [6] Getter, K. L., & Rowe, D. B. (2006). The role of extensive green roofs in sustainable development. HortScience, 41(5), 1276- 1285. [7] Hester, E. T., & Bauman, K. S. (2013). Stream and Retention Pond Thermal Response to Heated Summer Runoff From Urban Impervious Surfaces1. JAWRA Journal of the American Water Resources Association, 49(2), 328-342. [8] Kalnay, E., & Cai, M. (2003). Impact of urbanization and land-use change on climate. Nature, 423(6939), 528-531. [9] Kim, J., Choi, J., Choi, C., & Park, S. (2013). Impacts of changes in climate and land use/land cover under IPCC RCP scenarios on streamflow in the Hoeya River Basin, Korea. Science of the Total Environment, 452, 181-195. [10] Mentens, J., Raes, D., & Hermy, M. (2006). Green roofs as a tool for solving the rainwater runoff problem in the urbanized 21st century? Landscape and Urban Planning, 77(3), 217-226. [11] Nektarios, P. A., Amountzias, I., Kokkinou, I., & Ntoulas, N. (2011). Green roof substrate type and depth affect the growth of the native species Dianthus fruticosus under reduced irrigation regimens. HortScience, 46(8), 1208-1216. [12] Oberndorfer, E., Lundholm, J., Bass, B., Coffman, R. R., Doshi, H., Dunnett, N., et al. (2007). Green roofs as urban ecosystems: ecological structures, functions, and services. BioScience, 57(10), 823-833. [13] Scholz-Barth, K. (2001). Green roofs: Stormwater management from the top down. Environmental Design & Construction, 4, 63-70. [14] Sailor, D. (2008). A green roof model for building energy simulation programs. Energy and Buildings, 40(8), 1466-1478. [15] Takebayashi, H., & Moriyama, M. (2007). Surface heat budget on green roof and high reflection roof for mitigation of urban heat island. Building and Environment, 42(8), 2971-2979. [16] Teemusk, A., & Mander, l. (2007). Rainwater runoff quantity and quality performance from a greenroof: The effects of short-term events. Ecological Engineering, 30(3), 271-277. [17] USGBC, US Green Building Council. (2009). LEED Reference Guide for Green Building Design and Construction. Washington, DC: US Green Building Council.