SLIDE 1 Using LCA to facilitate the development
refrigerated display cabinets in the UK
Deborah Andrews
Dan Bibalou and Alan Foster London South Bank University.
SLIDE 2
Refrigerated Display Cabinets - RDCs
SLIDE 3
Refrigerated Display Cabinets - RDCs
SLIDE 4 Ellen MacArthur Foundatjon Circular Economy Introductory Kit
SLIDE 5 Ellen MacArthur Foundatjon Circular Economy Introductory Kit
SLIDE 6 Open loop recycling / upcycling / downcycling into another product system
Raw Material Acquisitjon Bulk Processing Engineered & Speciality Materials Manufacture & Assembly Use and Service Retjrement The Earth & Biosphere Treatment & Disposal
Closed loop recycling
Life Cycle Stage Fugitjve and untested residuals Airborne, waterborne and solid residuals Material, energy and labour inputs for process and management Transfer of materials between stages for product, includes transportatjon & packaging
Environmental Protectjon Agency (EPA) htup://www.epa.gov/ORD/NRMRL/lcaccess/lca101.htm
Recycling
Circular Economy
SLIDE 7 Open loop recycling
Raw Material Acquisitjon Bulk Processing Engineered & Speciality Materials Manufacture & Assembly Use and Service Retjrement The Earth & Biosphere Treatment & Disposal
Closed loop recycling
Life Cycle Stage Fugitjve and untested residuals Airborne, waterborne and solid residuals Material, energy and labour inputs for process and management Transfer of materials between stages for product, includes transportatjon & packaging
Environmental Protectjon Agency (EPA) htup://www.epa.gov/ORD/NRMRL/lcaccess/lca101.htm
Recycling
Circular Economy alternatjve business models
Remanufacture Reuse
Includes e.g. leasing selling a service
SLIDE 8 Using LCA to facilitate the development of a circular economy for refrigerated display cabinets in the UK
- 1. encourage remanufacturing and reuse of RDCs
SLIDE 9
In UK 9,200+ supermarkets and food outlets 800,000 RDCs per year - supermarket refrigeratjon uses 3.8 million kWh electricity and produces 1.5 M tCO2e untjl now emphasis of environmental impact - energy consumptjon and reductjon
SLIDE 10 Product Carbon Footprint Life Cycle Assessment
0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100%
3% 20% 98% 80%
Use phase Embodied
‘typical’ RDC - life cycle impact
SLIDE 11 Product Carbon Footprint Life Cycle Assessment
0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100%
3% 20% 98% 80%
Use phase Embodied
‘typical’ RDC - life cycle impact
SLIDE 12 Falkirk Telford Swindon Stoke on Trent Sheerness
supply all UK leading supermarkets and food retailers UK lead - remanufacture of RDCs
SLIDE 13
remanufactured RDCs are as good as / betuer than new RDCs
includes component upgrade – reduce operatjonal energy: replace fmuorescent lights with LEDs more effjcient refrigeratjon systems (compressors, evaporators, low GHG refrigerants etc.)
SLIDE 14 remanufactured RDCs are as good as / betuer than new RDCs
reuse / remanufacture
reduces materials use reduces energy inputs reduces environmental impact
SLIDE 15 remanufactured RDCs are as good as / betuer than new RDCs
reuse / remanufacture
reduces materials use reduces energy inputs reduces environmental impact
- nly 12.5% RDCs are remanufactured
SLIDE 16 1 2 3 4 5 6 7 8 9 500 1,000 1,500 2,000 2,500 3,000
Scenario B Scenario A Time (Year)
Carbon emissions (kg CO2e)
Scenario A RDC 1 RDC 1’ RDC 1’’ Scenario B RDC 2
Carbon Calculator – shows iteratjve refurbishment of RDCs reduces carbon output and costs
SLIDE 17
SLIDE 18 Using LCA to facilitate the development of a circular economy for refrigerated display cabinets in the UK
- 1. encourage reuse of RDCs and
use of remanufactured RDCs
- 2. assess materials suitability /
potentjal substjtutjon in Circular Economy
SLIDE 19
materials
average RDC – 450kgs 800,000 RDCs in UK 360,000 tonnes materials in use in sector some materials recycled - could this be increased? alternatjve end-of-life treatment?
SLIDE 20
materials in a typical RDC
metals
steel (stainless, carbon, galvanised), aluminium alloy, brass, copper
polymers – thermoplastjcs and thermoset plastjcs
rigid polyurethane foam (PUR), polystyrene (PS) & phenolic foams, polycarbonate (PC), polypropylene (PP), polyethylene (PE)
glass
plate, fjbre
MDF (medium density fjbreboard)
wood and other natural fjbres, urea formaldehyde resin
electronics
including precious metals
SLIDE 21
materials widely reused / recycled
metals
steel (stainless, carbon, galvanised), aluminium alloy, brass, copper
polymers – thermoplastjcs and thermoset plastjcs
rigid polyurethane foam (PUR), polystyrene (PS) & phenolic foams, polycarbonate (PC), polypropylene (PP), polyethylene (PE)
glass
plate, fjbre
MDF (medium density fjbreboard)
wood and other natural fjbres, urea formaldehyde resin
electronics
including precious metals
SLIDE 22
materials could be reused / recycled
metals
steel (stainless, carbon, galvanised), aluminium alloy, brass, copper
polymers – thermoplastjcs and thermoset plastjcs
rigid polyurethane foam (PUR), polystyrene (PS) & phenolic foams, polycarbonate (PC), polypropylene (PP), polyethylene (PE)
glass
plate, fjbre
MDF (medium density fjbreboard)
wood and other natural fjbres, urea formaldehyde resin
electronics
including precious metals
SLIDE 23
materials could be substjtuted?
metals
steel (stainless, carbon, galvanised), aluminium alloy, brass, copper
polymers – thermoplastjcs and thermoset plastjcs
rigid polyurethane foam (PUR), polystyrene (PS) & phenolic foams, polycarbonate (PC), polypropylene (PP), polyethylene (PE)
glass
plate, fjbre
MDF (medium density fjbreboard)
wood and other natural fjbres, urea formaldehyde resin
electronics
including precious metals
SLIDE 24
- 2. assess materials suitability / potentjal substjtutjon
in a Circular Economy use LCA – compare range of difgerent materials, manufacturing, installatjon processes, end-of-life scenarios and operatjonal energy inputs more comprehensive accurate than carbon ‘footprint’
SLIDE 25
PUR (rigid polyurethane foam) insulatjon
SLIDE 26
PUR sheets - constructjon industry and refrigeratjon units
SLIDE 27
for Circular Economy - can PUR be substjtuted?
established synthetjc materials
mineral wool glass fjbre
high-tech synthetjc materials
VIP (vacuum insulated panels) aerogel
natural
cork sheep’s wool cotuon
SLIDE 28 2 4 6 8 10 12 14
insulatjon panel - 1.8m (w) x 1.86m (h) x 40mm (d)
Product only - impact in mPoints
SLIDE 29 extending life - remanufacture / end-of-life - recycling, disposal USE – food storage and display materials / component manufacture electricity COOLING (refrigeratjon) PRODUCT (RDC) emissions pollutants
whole life cycle: integratjng energy & product chains
SLIDE 30 developing a Circular Economy - end-of-life scenarios
materials group materials end-of-life scenario reuse recycle compost landfjll / incin. established synthetjc materials PUR
chipped with resin - board chemical / pyrolysis
mineral wool
glass fjbre
high-tech synthetjc materials VIP
fjller / incinerate fjlm fjller / incinerate fjlm
aerogel
natural cork
sheep’s wool
cotuon
SLIDE 31 materials
propertjes & performance
PUR mineral wool Fibreglass VIP Aerogel Cork 160kg/m3 Sheep’s wool Cotuon Thermal conductjvity (W m-1 K-1) 0.022 0.033 0.033 0.008 0.014 0.042 0.042 0.038 Thickness (mm) 40 40 40 40 40 40 40 40 U value (W m-2 K-1) heat loss 0.47 0.66 0.7 0.2 0.32 0.8 0.8 0.7 Heat through insulatjon (W) 97 136 136 39 61 164 164 152 Energy use (kW.h yr-1) 567 794 794 227 380 959 959 888 CO2 from use (kg CO2e yr-1) 252 354 354 101 169 427 427 395 Volume of insulatjon (m3) 0.411 0.411 0.4 0.4 0.411 0.411 0.411 0.4 Density of insulatjon (kg m-3) 42 45 45 composite 109 160 14 19 Mass of insulatjon (kg) 17 18.5 19 33 (80% core, 20% fjlm) 45 66 6 8
SLIDE 32 Life Cycle Impact over 5 years
40mm insulatjon / difgerent thermal performance
20 40 60 80 100 120 140 160
recycle reuse or compost landfjll or incin.
SLIDE 33 Life Cycle Impact over 5 years –
same thermal performance / difgerent thickness insulatjon
20 40 60 80 100 120 recycle reuse or compost landfjll or incin.
SLIDE 34
Conclusion and future work
RDCs - PUR cannot be easily recycled or reused substjtute other materials – develop a Circular Economy? 40mm panels - thermal performance - on average impact of operatjonal energy is 14 tjmes higher than impact of insulatjon has a signifjcant impact on Life Cycle of all materials must be included in Life Cycle Assessment natural / organic materials – can be recycled / composted suggests - more suitable for Circular Economy but thermal performance is relatjvely poor - overall environmental load is high established synthetjc materials - thermal performance is relatjvely poor - overall environmental load is higher than PUR hi-tech synthetjc materials – excellent thermal insulatjon propertjes, fjller/core can be reused but fjlm can’t – is this suitable for Circular Economy?
SLIDE 35
Conclusion and future work
Structure and form: PUR is structural – can’t necessarily substjtute materials e.g. VIPs / Aerogel - present shape – can only be used for fmat panels (e.g. back) Will other materials fjll voids as well as PUR? do panels need to be redesigned for substjtute insulatjon materials? VIPs are relatjvely fragile – wastage could be higher – increase environmental load & cost Could PUR be blown into fjlm for easy disassembly? Could steel panels be coated with release agent? Could this be viable if commercial recycling facilitjes are developed? Will benefjts be short term as oil prices / PUR rise?
SLIDE 36 Conclusion and future work
Panels – same thermal performance / difgerent thickness
Natural materials compare favourably with synthetjc materials but panels are thicker Need to investjgate technical feasibility (structure, assembly and disassembly) impact of additjonal steel and all economic factors Finally… Developing a Circular Economy is very complex LCA is invaluable tool in development of CE –
- 1. clearly illustrates benefjts remanufacture
- 2. LCA results have raised rather than answered questjons
clearly highlighted areas for further investjgatjon
SLIDE 37
htup://vimeo.com/80559448