Global warming is happening, and 1.5 C is set to be
the maximum temperature we should achieve by 2050. The cause of global warming is
mainly greenhouse gas (GHG) emissions from fossil fuel-based production. Furthermore,
the building and construction sector contributes 37% of energy and process-related
carbon dioxide emissions (P.
Un Environment et al., 2024). Therefore, initiatives emerged worldwide,
namely the World Green Building Council
(WGBC). They advocate a completely Zero-carbon building by 2050 (D. Satola et al., 2021).
Net-zero carbon building is a balance between
renewable energy resources used by the building and the embodied carbon
produced by it (L. E. T.
Initiative). Still, some definitions also consider other factors, such as occupant and
transportation carbon emissions, to be reduced by renewable resources and
purchased carbon offsets.
Net zero building has various definitions and frameworks
across the countries. However, carbon emission reduction is the primary
objective of the design. According to D. S. Finnegan (2024). The design process of net zero carbon building
includes (1) understanding the operational energy used benchmark on each
building type and location, (2) calculating the LCA and EPD of material, (3) Analysing
the opportunity of the site to decide the strategy. For example, consider the
orientation, vegetation, and potential renewable resources; (4)
Evaluate cost and energy consumption; (5) Avoid creating new problems in the
maintenance process; and (6) Monitor the building’s performance regularly.
Based on P. S. Sharples (2024), several approaches can
be taken in designing a net zero-carbon building. The priority should be
minimising the embodied carbon that comes from materials transported until
their disposal. High-performance insulation and glazing
should be installed to reduce energy
consumption. Next, renewable energy options like solar, geothermal, etc.,
should be explored. Lastly, purchasing verified carbon offsets or investing in
carbon-captured installation can offset the remaining carbon.
Two case studies are
presented to help understand the concept of net zero carbon design in hot and
cold climates. For the hot climate, the DPR Construction Phoenix Regional
Office building is taken, whereas the Zero Energy Building (ZEB) Pilot House in
Larvik, Norway, is explained as an example in the cold climate environment.
Case Study 1: DPR Construction Phoenix Regional Office
1. Zero Carbon Building Policies
Phoenix is located in the United States of America
(USA). It is the capital city of the State of Arizona. USA contributes 23.83% of
carbon emmision or 431.85 MtCO2e (H. Ritchie et al., 2024). They have two similar approaches toward green
building, which are Zero-Energy Building (ZEB), assessed by the US Department
of Energy (DOE), and Zero Carbon Building provided by the United States Green
Building Council (USBGC). These initiatives are voluntary frameworks that aim
to support the reduction of GHG emissions both in new and existing buildings (D. Satola et al., 2022).
Zero-Energy Building was launched in 2015 and focused
on energy consumption. It calculated the use of Heating, Ventilation, Air
Conditioning (HVAC), lighting, vehicle charging, indoor transportation,
domestic hot water, and plug loads. The balance between energy use and production
is essential based on this framework. However, it does not specify the minimum Energy
Use Intensity (EUI) requirement and the building fabric. Moreover, it does not count
the embodied energy or emission as one of its scopes (D. Satola et al., 2022).
USBGC is a non-government agency that grants LEED Zero
Carbon Certification; published in 2018, the Zero Carbon schema includes measuring
the carbon dioxide equivalent (Co2e). Zero Carbon building is highly
energy-efficient. In addition, it aims to balance the amount of carbon dioxide emissions
released on an annual basis or even reach a negative carbon level because of its
renewable energy sources on-site and/or off-site (T. Usgbc, 2019).
Although Phoenix is part of Arizona State, most cities
have their targets regarding building carbon emission reductions. For instance,
Phoenix aims to have positive energy and materials for all new buildings in
2050 (C. O. Phoenix,
2024). Similarly, the USA projects that all existing
buildings will be included in the same year. While in 2050, Arizona set the
amount of carbon emissions reduction up to 208.000 MtCO2 (A.
S. University. et al., 2024).
2. Project Description
2.1.
Project
Overview
Table 1. DPR
Construction Phoenix Regional Office Overview
Architect |
SmithGroupJJR (architect), DNV KEMA Energy &
Sustainability (Energy Design and Building Performance) Bel-Aire Mechanical,
Inc. and Wilson Electric Services Corp (MEP Design-Assist Contractors) PK
Associates, LLC (Structural Engineer) |
Owner |
DPR Construction |
Year |
Renovation completed 2011, First built 1972 |
Size |
16,533 ft2 (1,536 m2) |
Height |
1 Story |
Building Type |
Class A Office 60 people |
Annual Hours Occupied |
2.080 (40
hours/week) |
Certification |
LEED BD+C v3 Platinum and Net Zero Energy
Building (NZEB) certification from the International Living Future Institute |
Budget |
$4,571,280 |
Building primary motivation |
1.
Cost-effective
2.
High-performing 3.
Aim for
ten-year payback |
Project Type |
Renovation |
DPR Construction renovated a neglected 1972 building as its Regional Office. It is located in Phoenix, Arizona, USA. DPR Construction also used 75% of the demolition and construction waste for the construction itself. Furthermore, this renovation is projected to meet a ten-year net zero energy investment payback (L. Reeder, 2016).
The renovation was completed in six months, from April
2011 until October 2011. After a year of evaluation of its sustainability
features, in December 2012, it achieved net zero energy in operations (L. Reeder, 2016). Recently, DPR Construction purchased 16,500 metric
tons of Verified Carbon Offsets certificate to neutralise the carbon emissions
in their three projects, including the Phoenix Regional Office (D.
Construction, 2022).
2.2.
Location
and Climatic Data
Figure 1. Climatic Data of Phoenix, Arizona (Ecoclmax, 2016) |
Figure 2. DPR Construction Phoenix Regional Office (Berkeley. et al., 2018) |
Table 2. Phoenix Climate Condition
Location |
222 N. 44th St. in Phoenix, Arizona, USA |
Latitude |
59.184N°N |
Longitude |
112.004°W |
ASHRAE Design Condition |
2B Hot and Dry (2021) |
Avg. Year Temperature |
24.2°C (DBAvg) |
Coldest Month |
15°C, Dec (MCDB) |
Hottest Month |
34.2°C, Juli (MCDB) |
Avg. Precipitation |
188mm |
Avg. Wind Speed |
2.8m/s |
3. Building Design and Services Strategies
3.1.
Challenges
and Solutions
Following the climate condition and the ten-year
investment payback period target, the building strategies include maximising
passive cooling and natural lighting, Optimising the building insulation and
reusable material, utilising photovoltaic energy resources and water-efficient
fixtures, and periodically controlling the energy used.
The passive design strategy includes deciding the
orientation of the building. The doors and windows are placed on the north and
east sides because the sun is less intense in those directions (L. Reeder, 2016) and 87 operable windows and roll-up doors provide
natural daylight and air circulation (Berkeley. et al., 2018). Moreover, all windows are controlled by a Building Automation
System (BAS) that adjusts the opening according to current climatic conditions,
such as wind speed and temperature from the local airport weather station data (L. Reeder, 2016). Besides the window, solar chimneys and shower towers
are also controlled by this system (Edc, 2012).
Figure 3. Cooling Tower on
the East Side of the Building (Berkeley. et al., 2018) |
Figure 4. An 87 Foot Long
Solar Chimney Vacuum the Hot Air Outside (L. Reeder, 2016) |
Figure 5. Passive Cooling System and Renewable Energy
Sources in The DPR Construction Building (L. Reeder, 2016)
The natural lighting system comprises 82 Sollar tubes that
reduce 70% of artificial lighting (Edc, 2012) and oversized windows. Additionally, a patio is
placed along the windows and acts as a connection between the outside and
interior of the building. Its planted covered roof serves as a barrier to
prevent dust, noise, and excessive sun exposure (L. Future, 2025). In addition, to overcome the low precipitation conditions,
water efficiency strategies, including the use of efficient sanitary fixtures,
drought-tolerant landscaping, and drip irrigation, are adopted (J. S. Robins,
2014).
Figure 6. Site and Roof Plan (L. Reeder, 2016) |
1. V panels on the parking’s roof 2. Patio 3. Entrance 4. Solar Tubes on the existing roof 5. Solar Chimney 6.Landscape |
3.2.
Renewable
Energy and Energy Use
According to a 2014 evaluation. The EUI is 80 kWh/m2/year, whereas the office baseline is 212.5 kWh/m2/year (L. Reeder, 2016). This means the energy consumption per metre square is lower than the average office building standard. These can be achieved because of several strategies, including adopting a shutoff button to eliminate the non-critical load. The last person in the office needs to push this button to reduce the energy used. Moreover, a monitor energy performance is available for all members to check in real-time (J. S. Robins, 2014). Domestic hot water also reduces energy consumption using a roof-mounted solar thermal system next to the solar chimney. In addition, existing inefficient mechanical units are replaced with LED light fixtures and daylight censors (Edc, 2012).
Figure 7. The use of
tubular daylighting reduces 70% of energy consumption (J. S. Robins,
2014) |
Figure 8. Building Energy
Performance Dashboard Accessible For Occupant Helps Control Their Behavior (Berkeley. et al., 2018) |
The DPR office uses a photovoltaic (PV) energy source. PV Panels are installed on top of the parking canopy. They consist of 326-235 Wdc modules with a ten-degree tilt. The system is connected to the grid so excess electricity can be credited to the building management. Moreover, this 79 kWh solar panel system can generate 142.871 kWh. Compared to the annual energy used, this building can collect 13.255 kWh of energy back to the grid (L. Future, 2025).
Figure 9. PV Panels on The Parking Roof, Courtesy of
Gregg Mastorakos (L. Future, 2025)
3.3.
Material
and Embodied Carbon
Material selection is closely related to Life Cycle
Assessment (LCA). LCA is used to calculate the building's performance in terms
of carbon emissions throughout its life cycle, from material extraction to end-of-life
processes, such as recycling (V.
Rodrigues et al., 2018). In this case, the DPR construction renovation
project recycled the demolition material and maintained most of the existing
structure. For example, the concrete masonry block wall, structural steel, and
roofing are retained. This resulted in a reduction of landfill waste by 252
tons. Additionally, it used bamboo for the screen wall enclosing the building, which
accounted for 3.35% of the material cost (Edc, 2012). Bamboo, Timber and bricks are examples of
regenerative materials that are low in carbon emission (P.
Un Environment et al., 2023).
Native desert plants such as Vines, Palo Verde trees, Agave
Cacti, Desert Spoon Shrubs, and Hesper aloe are used as they are more tolerant of
drought (L. Future, 2025).
3.4.
Lessons
Learned
The building aims to reduce energy consumption by
optimising the natural resources in the desert environment. However, collecting
airborne dirt on the water filter in the cooling tower is unavoidable. A
regular cleaning process is needed to overcome this issue (L. Reeder, 2016). In addition, automated windows produce noise that
affects occupant comfort (J. S. Robins,
2014).
Strategies to decrease energy consumption depend on
the occupant’s participation. For instance, pressing the shutoff button to
reduce non-critical load, participating in daily energy monitoring, and
tolerating the temperature threshold since the building adapts a passive
cooling system. These strategies demand continuous campaigns and education from
the top management.
4. Building Performance and User Satisfaction
Figure 10. The Comparison between Predicted, Actual
Energy Use, and Actual Energy Generated from Sollar Panel from January 2012
until February 2013 (J. S. Robins,
2014)
The graph shows that the energy use was lower than
predicted in the first year of operation. Moreover, there was an energy surplus
between the energy generated from Photovoltaic panels and the energy
consumption. This surplus can be distributed to the grid, therefore
accelerating the return on the investment from the ten-year target to only an eight-year
(L. Future, 2025).
Figure 11. 2014’s
Energy Used |
Figure 12. Energy
used between 2012-2013 (J. S. Robins,
2014) |
5. Conclusion
The Zero-Energy Building policy was reflected in the
DPR Construction Phoenix building objective. It is focused on minimising energy
use by optimising the site’s opportunities, such as solar radiation and wind. As
a renovation project, it reuses as much of 93,7% of the existing building
features as possible to lower the carbon emmision. It also monitored daily
energy used according to microclimate conditions as well as to encourage
occupants’ participation in reducing the electricity. Combining energy-efficient
strategies and renewable energy resources resulted in 8 years of investment
return.
Case Study 2: ZEB Pilot House Larvik, Norway
1. Zero Carbon Building Policies
Norway produces 0.15% of carbon emissions worldwide (H. Ritchie et al., 2024). It has become one of the lowest emittent countries because
of its hydropower, which comprises 95% of its energy resources (R. S. Jorge et al., 2013). Norway established a Zero-Energy Building (ZEB) scheme
in 2015. It uses Green House Gas (GHG) reduction as the key indicator that
focuses on the whole life cycle both for operational and embodied carbon. Furthermore,
in 2050, 95% of GHG emissions are expected to reach below the 1990 level for
all types of buildings (D. Satola et al., 2022).
The ZEB initiative was introduced by a research
organization which suggests 5 levels of ZEB according to the ambition level, including
(1) ZEB-O-EQ, which focuses only on the operation of the building, excluding equipment
or plug load; (2) ZEB-O, including all operational; (3) ZEB-OM, adding the
materials embodied carbon; (4) ZEB-COM, considering the GHG emission that comes
from the construction process as well; (5) ZEB-COME encompasses all aspect,
where the emmision can be offset by the use of renewable energy (D. Satola et al., 2022).
2. Project Description
2.1.
Project
Overview
Figure 13. ZEB Pilot House, Larvik, Norway (Archdaily,
2015)
The
second case study is in Norway. It is a two-story house for up to five members,
part of a Zero-Emission Building Pilot project in Norway. It aims to achieve
ZEB OM + Electric cars, where construction operations and materials production
emissions are balanced with the building's renewable energy. Plus, supplying
the user’s electrical vehicle. This building was completed in 2014 at 665
thousand US dollars for a 200m2 house. This research project has no occupants.
Therefore, the performance result may vary in the actual context (A. Sørensen et al., 2017).
Table 3. Project
Overview
Architect |
Brødrene Dahl
(energy concept), Optimera (building
construction), Snøhetta (architect), and the ZEB Research
Centre (energy and GHG emissions) |
Owner |
Brødrene Dahl
AS and Optimera AS |
Year |
2014 |
Size |
200m2
(2,152 square feet) |
Building Type |
Single-family
residential building. 4-5 member |
Certification |
ZEB-OM
Classification The European
Union Prize for contemporary architecture- Mies van der rohe award |
Budget |
5.8 million
NOK (or approximately $665,000) |
Building primary motivation |
Comfort:
indoor air quality and
daylight, environmental performance. |
Project Type |
New
construction, ZEB-OM + electric car |
2.2.
Location
and Climatic Data
|
Figure 15. Larvik Climate Zone (M. Manni et al., 2022) |
Located in Ringdalveien 18, 3270 Larvik, Norway,
this building is in a Temperate Oceanic Climate based on the Köppen-Geiger climate zone.
February is the coldest month when the temperature drops to -2.8°C (D. Climate, 2015).
Table 4. Larvik
Climate Condition
Latitude |
59°12’N |
Longitude |
10°15’E |
Köppen-Geiger |
Cfb, Temperate Oceanic Climate |
Avg. Year Temperature |
7°C (DBAvg) |
Coldest Month |
3.9°C, Jan
(MCDB) |
Hottest Month |
19.5°C, Juli (MCDB) |
Avg.
Precipitation |
974mm |
Avg. Wind
Speed |
3.7m/s |
(D. Climate, 2015); (A. Sørensen et al., 2017)
3. Building Design and Services Strategies
3.1.
Challenges
and Design Solutions
re 16. ZEB Pilot House Design Strategy (A. Sørensen et al., 2017)
Several strategies have been applied in the ZEB Pilot
House. Still, two main strategies in a cold-climate building are applied:
creating a high-performance building envelope with good insulation and air
tightness to reduce energy loss and minimize the energy used for the heating
system. Moreover, good indoor air circulation and
temperature are also among the project’s priorities.
Figure 17. Thermal Protection of The Building Envelope
on The North-West Facing Tilted Wall (A. Sørensen et al., 2017)
The fabric and insulation approach includes utilising
350 mm of glass wool and installing good U-values windows, doors, roof, walls,
and floor to ensure air tightness. Although the building is oriented to the
south-east, the big window on the north-south is covered by solar protection,
whereas the south side utilizes massive exterior cladding wood to prevent heat.
Also, a reused brick wall in the atrium adds some thermal mass. On the second
floor, aspen was used to handle the humidity by being installed as part of the
wall cladding. In total, nine different wall structures are used. Besides
reused bricks and glass wool, natural stone, timber, and low-carbon concrete
are also applied. Thermal resistance also increased when a crawl space is
provided underside the floor, which is mounted by reflective films (A. Sørensen et al., 2017).
Table
5. U-Value Coefficient in The
Building’s Insulation (A. Sørensen et al., 2017)
The heating load is 80% covered by a ground source to
a water heat pump, whilst 20% comes from a solar thermal collector on the roof.
In addition, heat recovery from air and grey water is collected and reused. The
figure below shows that at least six flows distribute water and air to the
building.
Figure 18. The Energy Supply Comes from Two Main
Sources, Solar Collector and Ground Source to Water Heat Pump (A. Sørensen et al., 2017)
The heat is distributed through an underfloor heating
system, which has only one radiator on each floor. Additionally, the
ventilation system uses grills and exhaust air heat pumps. Both supply heating
and cooling that are connected to a heat exchanger. Besides, all rooms have at
least one window that can be opened during the warm season (A. Sørensen et al., 2017).
Figure 19. Left: Shower Drain Shows One of The Grey
Water Heat Recovery Mechanisms. Right: Accumulator Tank as Outside Grey Water
Heat Recovery System (A. Sørensen et al., 2017)
Another
strategy is the water-efficient fixture. A 5,000-liter tank of rainwater
collection is provided for toilet flushing and irrigation (T. R. R. Writer,
2021). In addition, it has a controlled lighting and
heating system that can be adjusted as needed using smart home devices
connected to the website to reduce energy consumption.
Figure 20. Control System Panel for Solar Collectors (A. Sørensen et al., 2017)
3.2.
Renewable
Energy and Energy Use
The
photovoltaic system produces 19,200 kWh/year. It comprises 150 m2
solar panels with a 19-degree tilt and is oriented -45 to the southeast side to
optimize sun exposure. This renewable energy is connected to the local
electricity grid and battery bank. After eight years of observation, the energy
needed is 17,348 kWh/year. Still, the demand for electricity from PV systems is
reduced due to the energy generated from other sources, namely ground source
and solar collectors. Thus, only 7,142 kWh of electricity is taken from PV; the
rest is delivered to the grid.
Figure 21. Grid-connected solar PV System (A. Sørensen et al., 2017)
The
battery bank (48V at 600Ah) aims to increase the PV system's economic value.
Excess energy from PV-generated electricity can be converted to a selling price
that accelerates the return on investment of the construction cost.
Table 6. A Balance of Energy Generated from The PV System
and Other Heat Sources against Energy Need (A. Sørensen et al., 2017)
3.3.
Material
and Embodied Carbon
Over its 60-year lifetime, this building emits 2,650
kgCO2 eq. 36% comes from operational energy use, while 52% comes
from the building material. Additionally, 12% are electrical-related emissions (A. Sørensen et al., 2017). It was built with high-quality materials and a decent
way of working, ensuring that constant renovation will not be needed during its
lifetime (V. Vemula, 2021). According to A. Sørensen et al. (2017), who cited Rosochacki (2014), said that the
building's structural parts, such as walls and insulation, had the highest
emissions. Therefore, the fabric’s material choices were carefully considered.
Figure 22. Material Choices to Reduce Carbon Emissions and Improve Insulation (A. Sørensen et al., 2017)
Material choices are as follows: (1) Reused bricks in
the atrium can minimise carbon emissions compared to a new one; (2) timber and fibre-based
floor plate; (3) swimming pool made from reused steel container; (4) gabion or
other natural stone and timber as an exterior facade; (5) low carbon concrete is
also adopted, especially the use of strip foundation, to reduce the carbon
emissions.
3.4.
Lessons
Learned
As the project is a pilot project conducted by a
research initiative, gaining a complete and correct Environment Product
Declaration (EPD) from subcontractors and producers was challenging. Moreover,
it is a concern that the project investment is too high to be adopted in an
actual residential area. It also employs various digital tools in practice,
namely, Building Information Modelling (BIM), SimaPro, and Ecoinvent, which may
seem intimidating for some design teams and homeowners. The ambition of
achieving ZEB-OM closely depends on the intensity of electric vehicle use.
Since no actual user occupied the house, an exact measurement can not be analysed
(A. Sørensen et al., 2017)
4. Building Performance and User Satisfaction
Figure
23. Comparison Between Monthly Energy Generated and Energy Needed Plus PV Solar
Fraction (A. Sørensen et al., 2017).
This
research building has been evaluated for eight years (V. Vemula, 2021). The building needs 17.348 kWh of energy per year, or
EUI 86,1 kWh/m2. The remaining demand for delivered energy was calculated to be
7,142 kWh of electricity per year, with the highest
solar fraction in between May to August (A. Sørensen et al., 2017).
Table 7. Investment Payback Time Calculation (A. Sørensen et al., 2017)
In
the future, the building investment will cost 5.6 million NOK, or 1 million
more expensive than the Norwegian building code. However, due to the self-sufficient
energy generated and excess energy income, this building is projected to
achieve 35 years of investment payback period.
Figure
24. The Carbon Emission Balance Comparison from Renewable Electricity,
Operational and Embodied Carbon (A. Sørensen et al., 2017)
Regarding carbon emissions, 36% of emissions come from operational energy use, while 52% is from embodied carbon and replacements. Plus, 12% is the electric vehicle-related emissions. A reduction of 7,600 km of electric car use needed to be done to balance the emissions (A. Sørensen et al., 2017).
5. Conclusion
In cold climates, the capacity of material to prevent
heat loss is crucial. The compactness of the building will also determine how
much energy is used to heat the surface. The more compact the building is, the less
energy will be used (S.
Pelsmakers, 2015). Furthermore, well-insulated fabric and reusable heat
can be utilised to reduce energy consumption.
Comparative Analysis for Both Case Studies
The case studies show significant differences between
hot and cold climates, mainly from the U-value and R-value of the insulation. According
to S. Pelsmakers (2015), the U-value is the heat transfer rate through the material,
whereas the R-value is a material’s resistance to heat flow. The lower the U-value,
the less heat is transferred through the material, while the higher the
R-value, the more it is in resisting heat transfer (S.
Pelsmakers, 2015). Therefore, improving the performance of the
insulation based on the climate condition will reduce the energy consumption (I. Nardi et al., 2014).
DPR Construction office, located in the hot desert
climate, opts for passive cooling strategies. Moreover, based on I.
Institute (2025) The
2012 International Energy Conservation Code (IECC) Guide for Homes in Arizona, it
is suggested that the R-value minimum for walls is 13 m2K/W. The DPR
Office case study shows that the wall's 19 m2K/W R-value achieves
user satisfaction and can reduce energy consumption.
Meanwhile,
the Larvik house, in the cold climate, opts for a U value for windows and door
is 0.75 W/m2k. According to Ndvk (2023),
the required thermal transmittance for doors and windows is suggested below 1,2
w/m2k. It means that the windows and doors in the second case study
have already met the insulation standard in a cold climate area.
Both
studies emphasise embodied carbon. However, in the DPR Construction Office case
study, LCA was not included in the LEED assessment. In contrast, the ZEB Pilot
House emits 13,2 kgCO2 eq/m2 per year, which is predicted to achieve net zero
carbon within 60 years accumulated with the operational carbon and the use of
electric cars. However, the future occupant need to limit their travel time by 7,600
km. Embodied carbon significantly contributes to the total carbon emission (A. Houlihan Wiberg et al., 2014).
Therefore, precise EPD and LCA calculation should become crucial to net zero
carbon building.
The
case study had a metered system that can be regularly monitored via a website.
It helped measure daily energy use and encouraged occupant participation,
eventually creating a new habit of adjusting to a more energy-conscious
lifestyle.
Both case studies demonstrate the feasibility of
achieving net-zero carbon buildings in different climates using various
strategies. The DPR office highlights the effectiveness of renovation, passive
cooling systems, and plug load reduction. Meanwhile, the ZEB Pilot House
showcases the benefits of new construction, focusing on minimizing both
operational and embodied carbon.
Table 9. Comparison between Hot Climate and Cold Climate Buildings
Comparison |
Hot Climate |
Cold Climate |
Building |
DPR Construction
Phoenix Regional Office,
USA |
ZEB Pilot House Larvik, Norway |
Climate |
2B, Hot
and Dry (ASHRAE, 2011) |
Sandefjord, Torp warm and temperate (Koppen-Geiger) |
Avg. Temperature |
24.2°C |
7°C |
Building Type |
Office,
60 people |
Single-family residential building. 4-5 member |
Project Type |
Renovation |
New Construction |
Building Motivation |
Cost-effective, High performing,
10 y PBP |
ZEB-OM + electric car |
Minimize Embodied Carbon |
1. Reuse 93,7% original shell and structure 2. Renewable material: wood |
1. Reuse brick, steel container, railroad sleepers 2. Renewable material: timber, fibre, stone 3. Low-carbon material:
Low-carbon concrete 4. LCA, EPD |
Minimise Operational Energy Consumption |
1. Envelope R-Value: Walls:19 Roof:43 Windows: 0.15
(U-factor) 2.
Plug load reduction and monitoring |
1. Envelope U-Value (W/m2K) Walls: 0.111 Roof: 0.084 Windows&Doors: 0.75 2. Lighting & heating control system |
Maximise Use
of Renewable Energy |
PV
energy generated Thermal energy: Sollar collector |
PV energy generated Thermal energy: ground source, solar collector, grey water heat recovery, air-to-water
heat pump |
Offset Remaining carbon emission |
6,500 metric tons (cumulative) |
- |
Investment Payback Period |
8 Years |
35 years |
Net Zero Carbon Period |
9 years |
60 years |
Thermal Comfort |
20 °C (winter) 27 °C (summer) |
22-degree celsius |
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