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Environmental implications of composites John Summerscales

Environmental implications of composites John Summerscales

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Page 1: Environmental implications of composites John Summerscales

Environmental implications of composites

John Summerscales

Page 2: Environmental implications of composites John Summerscales

Outline of lecture• raw materials• production• fitness for purpose• end-of-use

Page 3: Environmental implications of composites John Summerscales

Consumption of materialsMaterial Production/Consumption (Mega Tonnes) Date

Steel 1107 2005

Aluminium 23.4 2005

Copper 12.4 2003

Zinc >10 2005

Timber EU-25 21.8 2003

Timber UK 7.5 2004

Plastics 100 2006

Plastics >300 20101

Plastics UK 4.7 2002

Bio-based polymers 0.7 20102

Bio-based polymers 1.7 20152

Composites WEur 1.54 2000

Composites UK 0.21 2000

1: http://dx.doi.org/10.1016/j.progpolymsci.2013.05.0062: http://dx.doi.org/10.1016/j.eurpolymj.2013.07.025

Page 4: Environmental implications of composites John Summerscales

Mtonnes of composites in USA

Page 5: Environmental implications of composites John Summerscales

Raw materials

• Thermoplastics, resins,carbon fibre, aramid fibreso primary feedstock = oilo potential for coal as feedstocko bio-based feedstocks

e.g. carbon fibres from rayon (cellulose)

• Glass (or basalt) fibreso primary feedstock = minerals

Page 6: Environmental implications of composites John Summerscales

Production of materials

• carbon fibres pyrolysed at 1000-3000°C*

o higher temperatures for higher moduluso greenhouse gases produced

• aramid fibres spun from conc.H2SO4 solutiono strong acid required to keep aramid in solution

• glass fibres spun from “melt” at ~1375°Co greenhouse gases produced

http://www.answers.com/topic/carbon-fiberhttp://www.answers.com/topic/kevlarhttp://www.answers.com/topic/fiberglass

Page 7: Environmental implications of composites John Summerscales

Component manufacture

• Net-shape production?o knitted preformso closed mould to avoid “overspray” or

equivalento dry fibres and wet resin (infusion vs prepreg)

for aerospace prepreg manufactureup to ~40% of material from roll may go to wastebecause fragment size and orientation not useful

resin film infusion uses unreinforced resinso orientation is not an issueand % usage only limited by labour costs

Page 8: Environmental implications of composites John Summerscales

Fitness for purpose

• does lightweight structurereduce fuel consumption?

• what is the normal product lifetime?o can it be designed for extended life/ re-use

etc

• do safety factorsunnecessarily increase materials usage?

Page 9: Environmental implications of composites John Summerscales

End of life: hierarchy of options: • first re-use

o consider re-use (or dis-assembly or recycling)at the design state

• re-cycleo potential for comminuted waste as filler

• Decompositiono pyrolysis/hydrolysis etco for materials recovery, e.g. Milled Carbon Ltd.o future: enzymes, ionic liquids, sub- and super-critical processes

• incinerationo with energy recovery

• finally landfillo only if all else fails.

Page 10: Environmental implications of composites John Summerscales

PET: poly ethylene terephthalate

HDPE: high density polyethylene

PVC: poly vinyl chloride

LDPE: low density polyethylene

PP: poly propylene

PS: polystyrene

other: polycarbonate, ABS, nylon, acrylic or composite, etc

Plastic Resin Identification Codes

Page 11: Environmental implications of composites John Summerscales

Plastic Resin Identification Codes

PA6 GF30/M20 FR: • polyamide-6

(caprolactam-based nylon)• 30% glass fibre• 20% mineral filler• flame retardant

Page 12: Environmental implications of composites John Summerscales

An alternative is compostingfor bio-based materials

• composting: biodegradation of polymers under controlled composting conditions

• determined using standard methods including ASTM D 5338 or ISO 14852o aerobic (with air present):

in open air windrows or in enclosed vessels

o anaerobic (without air): animal by-products or catering wastes

• biogas is ~60-65% CH4 + 35% CO2 + others

• 100 year GWP of methane = 23x that for CO2

*

* according to the Stern Review “The Economics of Climate Change” (2006),

but the short term effect is even greater.

Page 13: Environmental implications of composites John Summerscales

Digestion vs Composting

  bacteria (no fungi)Anaerobic digestor

  Aerobic composting bacteria and fungi

temperature:

50-60°C

chemical pulp - starch - starch/PCL-

PHA - PLA

thermophilic digestion

  industrial compostingchemical pulp - mechanical pulp - starch - starch/PCL - PBAT -PHA -

PLA

temperature: ≤35°C

chemical pulp - starch - starch/PCL-

PHAmesophilic digestion   home composting

chemical pulp - mechanical pulp - starch - starch/PCL - PBAT -PHA

outputs CO2 - humus digestate   compost CO2 - CH4 - N2O - humus

BG Hermann, L Debeer, B de Wilde, K Blok and MK Patel,To compost or not to compost: carbon and energy footprints of biodegradable materials’ waste treatment, Polymer Degradation and Stability, June 2011, 96(6), 1159-1171.

Page 14: Environmental implications of composites John Summerscales

Political drivers (EC)

• End of Life Vehicles (ELV) Directive (2000/53/EC)o last owners must be able to deliver their vehicle

to an Authorised Treatment Facilityfree of charge from 2007

o sets recovery and recycling targetso restricts the use of certain heavy metals

in new vehicles

• Waste Electrical and Electronic Equipment (WEEE) Directive (2002/96/EC)

Page 15: Environmental implications of composites John Summerscales

ELV targets• end of life vehicles generate 8-9 Mtonnes

of waste/year in the European Community

• 2006: o 85% re-use and recoveryo 15% landfill

• 2015:o 95% re-use and recoveryo 5% landfill

Page 16: Environmental implications of composites John Summerscales

ELV targets

• ELV targets were set to minimise landfill• total lifetime costs may be increased

o e.g. for composites:o thermoset manufactured at use temperature

but recycling is difficult

o thermoplastic processed at use + ~200°C could be recycled by granulating/injection

mouldingfor lower grade use

but higher GreenHouse Gases (GHG) early in life?

Page 17: Environmental implications of composites John Summerscales

Carbon fibres: incineration

• carbon fibres should burn to CO2

in the presence of adequate oxygen(with recovery of embedded energy)

• incomplete combustion may lead to surface removal and reduce diameter

• rescue services concerned by health riskof inhalable fibres released fromburning carbon composite transport structures

Page 18: Environmental implications of composites John Summerscales

Life Cycle Assessment

ISO14040 series standards

•The goal & scope definition

•Life Cycle Inventory analysis (LCI)

•Life Cycle Impact Assessment (LCIA)

•Life Cycle Interpretation

Page 19: Environmental implications of composites John Summerscales

Environmental ImpactClassification Factors:

ISO/TR 14047:2003(E) Azapagic et al

Acidification Acidification Potential (AP)

Ecotoxicity Aquatic Toxicity Potential (ATP)

Eutrophication / Nitrification Eutrophication Potential (EP)

Climate Change Global Warming Potential (GWP)

Human Toxicity Human Toxicity Potential (HTP)

Depletion of abiotic /biotic resources

Non-Renewable / Abiotic Resource Depletion (NRADP)

Stratospheric ozone depletion Ozone Depletion Potential (ODP)

Photo-oxidant formation Photochemical Oxidants Creation Potential (POCP)

Draft BS8905 adds Land Use

Page 20: Environmental implications of composites John Summerscales

Environmental Impact for Glass fibre production:

Problem?Issue?No impact?

Page 21: Environmental implications of composites John Summerscales

Recommended further reading• Y Leterrier, Life Cycle Engineering of

Composites, Comprehensive Composite Materials Volume 2, Elsevier, 2000, 1073-1102.

• W McDonough and M BraungartCradle to cradle: remaking the way we make things,North Point Press, New York, 2002.

• SJ Pickering, Recycling technologies for thermoset composite materials: current status, Composites Part A, 2006, 37(8), 1206-1215.