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Eco-compatible plastic March - 2009 Michael Stephens – Technical director 1 About Symphony Environmental Shares traded on ‘AIM’ of the London Stock Exchange also on Plus Market and Bank of New York and Mellon US ADR program The only dedicated public quoted company in oxo-biodegradable plastic technology Global distribution network. d2wTM is now in more than 50 countries worldwide The Global Brand Global Headquarters – Borehamwood, England -UK Investment in R & D and current studies on PET and Agriculture Films High Tech test facilities 2 Main board Nirj Deva, DL, FRSA, MEP Chairman Michael Stephen Commercial Director Nicolas Clavel Hugo Swire, MP Non Executive Non Executive Michael Laurier Ian Bristow Michael Stephens CEO Finance Director Technical Director 3 Isn’t plastic fantastic? 4 Using available resources Plastic is made from a by-product of oil. Less than 4% of oil is made into plastic. it makes good environmental sense to use it for plastic production, otherwise it could be flared off. 5 Environmental benefits of plastic Fossil fuel used to produce: A million square meters of cellophane A million square meters of PP Film Energy 180 tonnes 76 tonnes A million glass bottles A million PET bottles 230 tonnes 66 tonnes 60 miles of cast iron Pipe 60 miles of Plastic Pipe 2000 tonnes 270 tonnes 6 The benefits of plastic packaging Lightweight Flexible Strong/Durable Heat sealable Impervious to moisture Printable Recyclable Reusable By-product of oil refining but… 7 400 years *FACT PLASTICS CAN TAKE UP TO 400 YEARS TO BREAK DOWN TRUE 8 The Plastic Disposal Issue Current options on disposal of plastic waste: Traditional landfill Incineration Recycle Composting ONLY IF IT CAN BE COLLECTED 9 Added Value Solution The Insurance Policy d2w® Eco-compatible Plastic Technology Complete degradation 2 – 5 years after the end of the products’ predetermined useful life span* If littered, degradation can take place within a few short months when exposed to hot climatic conditions * Depends on product type and exposure conditions 10 Responsible use of plastic The Three R’s REDUCE: will reduce the burden of persistent plastic waste in the environment REUSE: based products can continue to be reused for a finite amount of time RECYCLE: based products can be recycled and made from recycled plastic polymers 11 d2w® Eco-compatible additive system The d2w oxo-biodegradable technology is a masterbatch system that is added with the basic polymer resin during the manufacturing process. No changes to extrusion process required. No impact on line speeds or plant maintenance. No requirement for special training for labour. It is just a process of “adding degradability” to conventional plastics 12 Eco-compatible plastic Overview d2w eco-compatible plastic will degrade, then biodegrade, to water, CO2, biomass and trace elements. It happens on land or sea, in the light or dark, in heat or cold, in whatever timescale is required. Residues Water CO2 Biomass NO ‘‘HEAVY METALS’’ 13 Types of Degradable Polymers Hydro-Biodegradable Oxo-Biodegradable H2O – Uptake Enzyme mediated or not Functional Fragments O2 – Uptake Catalyst Oxidized Fragments Exo-Endo Enzymes Exo-Endo Enzymes CO2, H2O, Cell biomass CO2, H2O, Cell biomass Polyesters Polyolefins Polyamides Polyvinylalcohol Polysaccharides Lingin 14 Degradability Properties of the ideal biodegradable plastic IPa,b Induction periods during which no change in mechanical or chemical properties occur Eb Elongation at break + Fragmentation (embrittlement) G. Scott, Polymers and the Environment, Royal Society of Chemistry, 1999, Charpter 5 15 Eco-compatible plastics The process Polyolefin consists of long entangled molecular chains. There is a backbone of Carbon atoms to which Hydrogen atoms are attached. The catalytic effect of the d2w additive breaks these chains by generating free radicals. Theses free radicals combine with the available oxygen atoms and create hydroperoxides -which are the precursors to full bio-degradation. Carbon degradation is affected by heat, light, stress and air Hydrogen Oxygen 16 Eco-compatible plastics The process The resulting short chain hydroperoxides are available for consumption by micro-organisms. Carbon Hydrogen Oxygen Micro-organism (Stenotrophomonas sp., Pseudomonas sp., Rhodococcus sp., Acinetobacter sp. etc) 17 Eco-compatible plastics The Results After the degradation process the harmless residues are CO2, H2O and Biomass. Carbon Hydrogen Oxygen Micro-organism (Stenotrophomonas sp., Pseudomonas sp., Rhodococcus sp., Acinetobacter sp. etc) 18 Eco-compatible plastics The process Polymer First stabiliser Second stabiliser Prodegradant trigger Prodegradant trigger - The catalytic action creating the free radicals is arrested and controlled by two stabiliser packages. The first stabiliser protects the prodegradant trigger transition during the manufacturing process. The second stabiliser ensures that the finished product fulfils its functionality and sustains an adequate shelf life. 19 Evidence and facts Oxo-biodegradable plastic 7 days in bio fertilizer Normal plastic 7 days in bio fertilizer 20 Evidence and facts Oxo-biodegradable plastic 60 days in solid compost 21 Certification European Normalization The Official Definition Biodegradation Degradation of a polymeric item due to cell-mediated phenomena. Oxo-biodegradation Degradation identified as resulting from oxidative and cell mediated phenomena, either simultaneously or successively. “Terminology in the field of degradable and biodegradable Polymers and Plastics” CEN TC 249/ WG 9 22 Facts Degradability Test Methods There are five test methods, including CO2 evolution to measure degradability in plastic packaging materials. Melt Flow Index; (MFI) this comparative test detects alterations in the molecular structure of a plastic material after being subjected to accelerated weathering. Elongation at Break: this comparative test measures the tensile strength of a material after being subjected to accelerated weathering. Molecular Weight; this comparative tests measures the reduction in molecular weight after accelerated weathering. Carbonyl Index: this method detects the creation of carbonyl groups within the plastic material indicating degradation through oxidation after accelerated weathering. It is comparative, but unlike the alternative tests it is nondestructive. Thus a sample can be placed back in any environment (aqueous, heated, UV radiated) and then be subjected to further testing. Predicts life expectancy. We predominantly utilise carbonyl testing as it provides a clear indication of oxidation and allows successive testing of samples exposed to extended weathering exposure. 23 Evidence and facts Melt Float Index - MFI MFI increase by > 4,000 % 24 Evidence and facts RAPRA Test 46095 April 2006 AN0068 99% LDPE + 1% d2w additive 7 Days UV Exposure Test No. Tensile Strength at Peak (Mpa) Enlogation at Break (%) 2 5 4.20 9.25 0.05 0.05 Mean 6.73 0.05 The samples were very fragile and the initial grip separation was reduced to 90 mm. The elongation results are technically too small to be accurate when measured with a laser extensometer. Meets ASTM 5510 elongation at break of less than 5% 25 Evidence and facts Elongation at Break Black d2w recycled trash can liner 1.2mil CRIQ File No 640-PE36987 (technical Report) Evolution of Elongation Meets ASTM 5510 elongation at break of less than 5% 26 Evidence and facts Molecular weight Black d2w recycled trash can liner 1.2mil CRIQ File No 640-PE36987 (technical Report) A reduction of molecular structure from 225,000 to < 5000 Mw– confirms this is no longer plastic 27 Evidence and facts Molecular Weight Rapra confidential technical report 46303 Sample Run No Mw Mn Mw/Mn %<5,000 Polyethylene samples 99% 0 days (RTL 8400/1) B2930 B2934 76,900 77,300 14,900 14,500 5.2 5.3 6.9 7.1 7 days heat 99% PE (RTL 8400/3) B2932 B2935 4,560 4,510 1,290 1,300 3.5 3.5 67.7 68.1 A reduction of molecular structure from circa 77,000 to < 5000 Mw – confirms this is no longer plastic 28 Evidence and facts FTIR - Carbonyl index Confirmation of relationship of carbonyl index to elongation at break. 29 Evidence and facts FTIR - Carbonyl index Explanation Bandol UV Ageing LDPE Films- Comparison of Elongation at Break and Carbonyl Optical Density 120 0.02 0.018 100 0.016 Delta EaB (%) 0.012 Embrittlement Point 60 0.01 0.008 )Delata OD (1713cm-1 0.014 80 )LDPE Control (Tensile )LDPE + 1% 93389 (Tensile )LDPE Control (Optical Density )LDPE + 1% 93389 (Optical Density 40 0.006 0.004 20 0.002 0 0 50 100 150 200 250 300 350 400 450 0 500 5% Ageing Tim e (Hours) 30 Evidence and facts Carbonyl index by FTIR Films A (corn) and B (Melon) Oven Test at 60°C FTIR test A B Film ¼: in open air Film 5/8 :in the soil humid close cap Film9/12 :in dry soil with close cap Film 13/16: in dry soil without cap 31 On- Going Testing Three Year Compilation of Testing 32 Direct food contact safety All grades of d2w are compliant with the requirements of: The European Union 2002/72/EEC regulations for Direct Food Contact and all amendments. The FDA requirements for direct food contact materials. ANVISA requirements for Brazilian Direct Food Contact Safety. The d2w materials have successfully passed European Union migration tests. Confirmed by US owned - Smithers/RAPRA. FDA compliance confirmed by US law firm Keller and Heckman ECO-Toxicity All grades of d2w comply with the European Normalisation EN 13432 Ecotoxicity Section. Which confirms that no harmful residues remain after total degradation of the material. ( Tested by OWS, Gent, Belgium) The Brazilian Report “Program for Composting Oxo-biodegradable Plastic Residues” confirms that no harmful residues occur in compost after degradation. 33 French Mulch Film trial Official French Government assessment 34 Evidence and facts d2w vs Mater-bi co2 evolution Hydro mulching film Oxo mulching film 35 Evidence and facts Confirmation of EN13432 - (ASTM D6400) Shopping bag independant test done by public laboratory using normalized condition ASTM 6400 /EN 13432 36 Evidence and facts Confirmation of CO2 evolution in comparison to Cellulose 37 Evidence and facts Confirmation of EN13432 - (ASTM D6400) The film after oxidation (300h wet and dry Cycle) has reached a level of 82,3% of biodegradation compared to the reference cellulose. 38 Recycling Polymer Training Limited Recycling Study August 2008. CONCLUSIONS The results indicate that the Elongation at Break values of the sample plaques containing the various proportions of d2w regrind have similar values before and after ageing (both thermal and QUV). This suggests that incorporating d2w recyclate within a non degradable polymer matrix does not lead to the accelerated degradation of the resulting product. Under QUV ageing there is a progressive decline in EaB value from 0 to 144 hours ageing, but the decline is broadly the same across all d2w compositions. This suggests that any degradation effect is due to inherent loss of polymer property rather than due to an acceleration effect linked to d2w inclusion rate. It can be concluded that waste plastic materials containing d2w oxodegradable additives can be added into both non degradable and degradable formulations without accelerating the degradation of the resulting product. 39 Recycling Effect of d2w level in recyclate level on Elongation at Break after Thermal Ageing 40 Conclusion Plastic Packaging (including carrier bags) Plastic products made with d2w® eco-compatible technology will totally degrade by a process of oxidation leading ultimately to biodegradation. Plastic products made without d2w® eco-compatible technology will totally degrade by a process of oxidation leading ultimately to biodegradation, but in several decades. List of main evidences: Biodegradation (Applus) Compostability (CRIQ) Degradation in soil (ADEME/AGRICE) Eco-toxicity (OWS, Ecosigma) Food contact (RAPRA) Recycling (PTL) 41 www.degradable.net Eco-compatible Plastic Technologies “IN HARMONY WITH THE ENVIRONMENT” 42