embodied energy lecture 702-865 2009
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Embodied Energyin a life cycle context
Dr Robert Crawford
Faculty of Architecture, Building and PlanningThe University of Melbourne
www.ch2.com.au
Environmental SystemsSemester 2, 2009
theoretical overview & case studiesin the built environment
building environmental loadings and energy use
what is embodied energy?
the embodied energy context
strategies for reducing embodied energy
case studies and example calculation
why take a life cycle approach?
what is life cycle energy?
strategies for optimising life cycle embodied energy
life cycle energy examples
assessment tools
overview
Environmental Systems, September 2009
32% of world resources
12% of water consumption
40% of waste to landfill
40% of energy consumption
40% of air and GHG emissions
(OECD 2003)
building environmental loadings
Images source: Googleimages, 2008 Environmental Systems, September 2009
http://members.cox.net/slsturgi3/population_growth.gif
resource demand driven by population growth
20096.8 billion
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http://www.peakoil.org.au/charts/world.energy.consumption.1965-2007.gif
trend in world energy consumption
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6%
9%
15%
16%
21%
33% Cooking and Hot water
Equipment
Lighting
Ventilation
Cooling
Heating
commercial building operational energy use
Source: Australian CommercialBuilding SectorGreenhouse Gas Emissions 19902010, AGO 1999
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building operational efficiency
improvements to building resource consumption have
typically focused on the operational phase, particularlydirect fossil fuel and water consumption
efficiency measures are reducing household energy andwater consumption, not per capita
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operational energy efficiency strategies
planning and design
orientation
insulation
natural ventilation
thermal mass
shading
solar (electric and thermal)
wind
geothermal
passive
active
building life cycle
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Maintenance
energy
(1%)
Embodied energy
(initial)
(43%)
Operational
energy
(45%)
Renovation/
refurbishment
(9%)
Construction
energy
(2%)
building life cycle energy consumption
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The energy required by all of the activities associatedwith a production process and the share of energy used
in making equipment and other supporting functions(i.e. direct and indirect).
(after Treloar, 1994).
embodied energy
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raw material extraction and processing
material/component manufacture
transport
construction/manufacture
banking
insurance
marketing
communication services
accommodation
etcetera
what does embodied energy include?
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stage 0 stage 1 ...
upstream
stage 2 stage
direct energy indirect energy
direct
energy
direct
energy
direct
energy
direct
energy
Construction productsproductsproducts
Downstreamincludes building use - not as complex as upstream
embodied energy
Source:Crawford,2005
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process analysis
- based on physical quantities
- up to 90% incomplete
input-output analysis
- based on financial quantities (GJ energy / $1 product)
- systemically complete, unreliable
hybrid analysis
- combines process and input-output analysis
- systemically complete and more reliable
quantifying embodied resource requirements and impacts
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Construction
construction system boundary
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the supply chain is complex
Slide removed from handouts
Commercial buildings:
steel 9.3%
concrete 8.7%
road transport 3%
Residential buildings:
ceramic products 11.3%
concrete 9.3%
metal products 8.2%
where is most energy used?
Initial findings, based on input-output data:
- Residential buildings: 10.6 GJ/$1000
- C ommercial buildings: 9.98 GJ/$1000
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most comprehensive available
developed by the late A/Prof Graham Treloar (mid 90s)
based on:
- energy intensities of specific construction materials (using the mostdetailed database currently available in Australia)
(GJ of energy per m3, m2 or t of material)
- national average statistical data (input-output - includes capitalinputs, imports, minor goods and services)
hybrid embodied energy model
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calculating initial embodied energy
1) specify materials (types, thicknesses and quantities)
2) multiply individual material quantities by respective material
energy intensities (GJ of energy per m3, m2 or t of material)
3) add energy for minor goods and services using input-output data
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3-storey commercial office building
location: Melbourne
floor area: 11 600m2 GFA
Embodied energy:
25.8GJ/m2 GFA (300 000GJ)
46 years of operational energy
(0.558GJ/m2/year)
case study Toyota Head Office
source: www.toyota.com.au
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0 2 4 6 8 10
Structure group
Finishes
Substructure
Roof
Windows
Direct energy
Other items
GJ/m2
other items 31%
structure group 22%
windows 1 3%
direct energy 5.3%
embodied energy, by element
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0 2 4 6 8 10
Steel
Concrete
Other metals
Ceramics
Carpet
Glass
Plasterboard
Plastic
Paint
Timber products
Direct energy
Other items
GJ/m2
embodied energy, by material
other items 31%
steel 3 0%
glass 1 3%
concrete 6%
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building embodied energy equates to:
- 20 to 50 years of operational energy
- up to 50% of lifetime energy use (50 year building life)
typical embodied energy:
- 10 to 20 GJ/m2 GFA residential
- 20 to 30 GJ/m2 GFA commercial
energy embodied in buildings
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Residential buildings:
direct (on-site) energy -
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increasingly significant due to improved operational efficiencies
value of resources increasing
prices will rise, supply may be restricted
energy water resources waste disposal
potential for future carbon taxes/trading
demand needs to be managed for sustainable development
embodied resources
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production of energy releases greenhouse gas emissions
emission of GHGscontributes to global warming
on average, 60kg CO2 emissions released per GJ of energy produced
equates to 240t CO2 to construct an average house
over 200 times volume of average house
4.8 million balloons
environmental impacts from embodied energy
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Up to 90% of impacts are locked in
at the design stage
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Reduce use of materials
- quantity (eg. reduce building size)
- particularly those with high EE
- use alternative materials with lower EE
- rationalise design
- avoid redundant structure and facilities
reducing embodied energy reduce
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0
10
20
30
40
50
60
70
80
90
100
1950 1960 1970 1980 1990 2000 2008
Floorareaperperson(m
2)
Floor area per person has almost quadrupled
reducing embodied energy reduce
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Reuse materials in place
design for adaptive use
structural integrity issues
fit for future use?
reusing existing structure can save up to 50% of total building EE
reusing materials can save up to 95% of EE of new materials
Reuse materials from elsewhere
this site or another project
design for disassembly
time and cost to make good
can save up to 90% of EE of new materials
(depends on transport and extent of making-good)
energy required for transport, installation
reducing embodied energy reuse
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Use/specify recycled materials
design for disassembly
EE saving depends on transport, re-processing energy
Use/specify materials with recycled content
e.g. concrete with flyash / recycled aggregate
Use/specify renewable materials
t imb er
b amboo
biomass waste (eg. bio-plastics)
reducing embodied energy recycle
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prefabricated modular steel v concrete
Source: Fender Katsalidis Architects
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prefabricated modular steel v concrete
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0
10000
20000
30000
40000
50000
60000
Steel Concrete
Construction system
Embodiedenergy(GJ)
Staircase
Floor tilling
Doors & windows
Roof
Internal walls
Ceiling
External cladding
Floor panels
External walls
Columns & beams
benefits from material reuse
81% energy saving from reuse of steel
influenced by reusability (disassembly)
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0
10
20
30
40
50
60
70
80
90
100
Volume Weight Embodied Energy
Percentage
Steel Concrete
Deakin University,
Waterfront Campus,
McGlashan & Everist,
1995
Church conversion, Glenlyon
Multiplicity 2004
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Melbourne GPO, 2001
Melbourne GPO
Williams Boag, 2004
embodied energy calculations
Example
Example: concrete floor
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Element description: concrete floor slab, carpeted
Functional Unit: one square metre of floor
Materials: concrete 32MPasteel reinforcementnylon carpet
example: concrete floor
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Embodied Energy Calculation:
* equivalent to fuel needed to travel by car for 818km
Assumptions:
slab 150mm thick
100kg steel per m3 concrete
example: concrete floor
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embodied energy intensities
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Slide removed from handouts
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Potential limitations
assessment method error tolerances (+/- 20%) = 2.2GJ 3.3GJ
Evaluate implications (substitute materials, details)
other floor materials e.g. timber
other floor covering materials e.g. tiles
Opportunities for optimising EE in this application
using reused/recycled materials (concrete)
using recyclable materials
material durability & expected life
example one: concrete floor
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Brick veneer Weatherboard
embodied energy of building assemblies
V
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initial embodied energy
important to assess life cycleimpacts
building life cycle
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ensures the multiple environmental and resource issuesacross the entire life cycle of the product are identified
helps to ensure reducing waste at one point does notsimply create more waste at another point in the life cycle
a life cycle approach
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embodied energy (initial and recurring)
operational energy
maintenance energy
end of life energy (reuse, recycling, disposal)
life cycle energy
Environmental Systems, September 2009
Embodied Energy
Building A appears the best choice
Life Cycle Energy
Building B consumes less energyoverall
Building A Building BBuilding A Building B
GJ GJRefurbish
Operation
EmbodiedEnergy
EmbodiedEnergy
a life cycle approach
Environmental Systems, September 2009
commercial building life cycle energy
< quantum leaps
indicate periods
of refurbishment
^ gradient gives
operational
energy< initial
construction
embodied energy
0
5
10
15
20
25
30
35
0 10 20 30 40
Time (years)
Lifec
ycleenergy(GJ/m2)
building life cycle energy
(GJ/m2)
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reduce non-renewable resource use
design for energy efficiency
specify low-impact materials
design for quality and durability
design for reuse and recyclability
reducing life cycle energy
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Lowering initial EE is not always ideal
Consider the life cycle implications of this on:
recurring EE (replacement)
maintenance energy
operating energy
Life cycle EE is affected by:
material durability
anticipated life (replacement cycle)
a life cycle approach to embodied energy
Environmental Systems, September 2009
design for disassembly
select materials for durability, long life and recyclability
look to the future - use/specify renewable materials
t imb er
b amboo
bio-plastics
most importantly consider life cycle impacts
optimising life cycle embodied energy
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life cycle view =maximum benefits
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Slide removed from handouts
assess building componentsand systems
often, efficiency and design improvements that reduce operationalresource requirements or impacts come at the expense of greaterembodied or life cycle requirements or impacts
e.g. double / triple glazing reduces building operational energyrequirements (compared to SG)
BUT, increases embodied resource requirements(materials, energy, water and associated impacts)
key question does it provide a net life cycle benefit?
crucial to assess/consider life cycle environmental impacts toensure net environmental benefits are achieved
ensuring environmental outcomes are not compromised
Environmental Systems, September 2009
Brick veneer Weatherboard
life cycle energy of building assemblies
V
Environmental Systems, September 2009
calculating life cycle embodied energy
1) specify material useful life (maintenance or replacement period)
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calculating life cycle embodied energy
2) calculate combined initial and recurring embodied energy
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life cycle embodied energy life cycle embodied energy of floor assemblies
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0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
4.0
4.5
5.0
GJ/m2
Elevated timber
floor
110mm concrete
slab on ground
205mm Hollow
Core precast
flooring
100mm elevated
concrete slab,
permanent
formwork
Recurrent embodied energy
Initial embodied energy
life cycle energy of floor assemblies
quantum leaps indicatemaintenance or materialreplacement
gradientrepresentsoperationalenergy
initial embodied energy
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0
1
23
4
5
6
7
8
9
10
0 5 10 15 20 25 30 35 40 45 50
Years
GJ
Elevated timber floor Concrete slab on ground
predicted total cooling energy saving: 280 GJ/year (83%)
PCM (in s/steel balls) contribute to some of this
however, 23 t of s/steel = 10,190 GJ embodied energy
36 years energy payback
CH2 cooling system embodied impacts
www.ch2.com.au
0
200
400
600
800
1000
1200
1400
1600
1800
2000
EE
(GJ)
2 4 6 8 10 12 14 16 18 20
Years
Life-cycleenergy(GJ)
EHWS
GHWS
GIHWS
SEHWS
SGHWS
life cycle energy of hot water systems
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-60
-40
-20
-
20
40
60
0 2 4 6 8 10 12 14 16 18 20
Years
PrimaryEnergy(GJ)
BiPV c :Si BiPV c :Si HRU BiPV a :Si HRU
life cycle energy of photovoltaic systems
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0
10
20
30
40
50
60
70
80
90
100
High R is e 7 -Star Ho us e Sub urban
Apartment
2008 House
Energy
(GJ
percapita)
Operational Energy
Embodied Energy
Travel Energy
Total Energy
annualised residential life cycle energy
Environmental Systems, September 2009
-200,000
200,000
600,000
1,000,000
1,400,000
1,800,000
2,200,000
EE 5 10 15 20Life-CycleEnergyOutput(G
J)
850 kW wind turbine
3.0 MW wind turbine
life cycle energy of wind turbines
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0
500,000
1,000,000
1,500,000
2,000,000
2,500,000
3,000,000
3,500,000
4,000,000
4,500,000
1 4 7 10 1 3 16 1 9 22 25 28 3 1 34 3 7 40
Time (years)
Lifecycleenergy(GJ)
Vehicle operationalVehicle manu. & maint.CRC - road typesPCFDACompDSAG
DSABACB
direct and indirect energy of road construction and use
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direct and indirect CO2 emissions of pipe systems
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0.0
0.3
0.6
0.9
1.2
DICL China
DN600
DICL Aust.
DN600
DICL China
DN450
DICL Aust.
DN450
tCO2-epermo
fpipe
indirect emissions
direct emissions
raw mat. trans.
pipe transport
cement lining
embodied CO2
emissions of concrete railway sleepers
Environmental Systems, September 2009
0 50 100 150
Sleeper
Tendons
Fastenings
Direct emissions
Other items
t CO2 -e per km of track
process values
input-output values
0
500
1000
1500
2000
2500
3000
3500
4000
0 10 20 30 40 50 60 70 80 90 100
Years
tCO2-eperkm
Concrete (C4)
Timber (T4)
Timber 50 (T8)
Timber 96 (T12)
sleeper replacement
decay emissions
life cycle CO2
emissions of railway sleepers
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building embodied water equates to:
- 20-80 years of operational water
- up to 60% of lifetime water use (50 year building life)
typical embodied water:
- 10-20 kL/m2 GFA residential (4-8 times building volume)
- 20-30 kL/m2 GFA commercial
water embodied in buildings
Environmental Systems, September 2009
LISA
SimaPro
Ecotect
LCADesign
GaBi
life cycle assessment tools
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LISA
Environmental Systems, September 2009
Project
details andparameters
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LISA
Specifyconstruction
elements
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LISA
Specify
fit outelements
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LISA
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Specify
appliances
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LISA
Specify
usage
details
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LISA
Specify
maintenance
requirements
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LISA
Specify
materialre-use
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LISA
Specify
material
transport
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LISA
inputs andoutputs by
material
quantity
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LISA
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Project
quantities
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LISA
Impact
assessmentby life-cycle
stage
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LISA
Range of
impact
categories
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LISA
Breakdown
of life-cycle
stage
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LISA
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SimaPro
Specify
assembliesor elements
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SimaPro
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Select &quantify
materials
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SimaPro
Select
materials/
processes
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SimaPro
Material
inputs &
outputs
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SimaPro
assessment
by impactcategory
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SimaPro
Impacts byproduct
stage
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SimaPro
Comparison
of twoproducts
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SimaPro
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Ecotect
Environmental Systems, September 2009
consider source of materials
maximise value of resources minimise wastage
reuse and/or recycle existing materials
maximise opportunities for reuse, through design
consider durability of recycled/reused materials
consider maintenance and replacement requirements
consider life cycle resource requirements/impacts
consider on-going implications of design decisions
summary
Environmental Systems, September 2009