BIOPLASTICS: Basics. applications. Markets.

BIOPLASTICS BASICS. APPLICATIONS. MARKETS. MICHAEL THIELEN

First edition, 2012

Polymedia Publisher GmbH, Mรถnchengladbach, Germany www.polymedia-publisher.com

Dr.-Ing. Michael Thielen: Biokunststoffe - Grundlagen. Anwendungen. Märkte. © 2012 Copyright Polymedia Publisher GmbH Mönchengladbach, Germany First edition Design, layout and typesetting: Mark Speckenbach, Julia Hunold printed by: KS PRINTING All of the information published in this book has been assembled based on the best of the author’s knowledge and understanding. Nevertheless the possibility of errors or omissions cannot be excluded. No responsibility is accepted, nor any guarantee given, with regard to the accuracy of the information provided. The author and the publishers therefore accept no liability that may arise as a result of this information, or part thereof, being used.

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The URLs given in the book point to Internet web sites. The author and the publisher accept no responsibility for the information contained in these web sites. Neither can any responsibility be accepted for the accuracy or completeness of that information, or for the fact that it may or may not be up to date.

ISBN 978-3-9815981-1-0 www.polymedia-publisher.de

PREFACE Petroleum is not an inexhaustible resource, and it is becoming ever more expensive. Burning of petroleum products (including plastics) has an impact on climate change. Bioplastics can offer an alternative in this regard.

Bioplastics are on the one hand biobased plastics (produced from renewable resources) and on the other hand may well be biodegradable plastics. Many bioplastics meet both of these criteria.

This book is based on numerous articles in the bioplastics MAGAZINE trade publication as well as on various talks, presentations and university lectures that have been given by myself in recent years.

It is intended to offer a rapid and uncomplicated introduction into the subject of bioplastics, and is aimed at all interested readers, in particular those who have not yet had the opportunity to dig deeply into the subject, such as students, those just joining this industry, and lay readers. It gives an introduction to plastics and bioplastics, explains which renewable resources can be used to produce bioplastics, what types of bioplastic exist, and which ones are already on the market. Further aspects, such as market development, the agricultural land required, and waste disposal, are also examined.

An extensive index allows the reader to find specific aspects quickly, and is complemented by a comprehensive literature list and a guide to sources of additional information on the Internet.

The author and the publishers express their thanks to all of the companies who have made it possible, through their advertisements, to publish this book at the lowest possible retail selling price. It should be made clear, however, that these companies have had no influence on the contents of the book. The author also expresses his thanks to the FNR (Agency for Renewable Resources) within then German Federal Ministry of Food, Agriculture and Consumer Protection for their support and excellent cooperation.

Mรถnchengladbach, Germany, February 2012 Michael Thielen |3

TABLE OF CONTENTS 1 Bioplastic - what is it exactly? . . . . . . . . . . . . . . . . . . . . . . 6 1.1 Fundamentals. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6 1.2 Bioplastics. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7 1.2.1 Biobased plastics . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8 1.2.2 Biodegradable plastics. . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8 1.3 Biobased plastics - why? . . . . . . . . . . . . . . . . . . . . . . . . . . 10 2 Renewable resources . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12 2.1 Introduction. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12 2.2 Natural Polymers . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12 2.2.1 Polysaccharides (carbohydrates). . . . . . . . . . . . . . . . . . . . 12 2.2.2 Proteins . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13 2.2.3 Lignin. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13 2.2.4 Natural rubber. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13 2.2.5 Other. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 13 2.3 Other biogenic materials . . . . . . . . . . . . . . . . . . . . . . . . . . 14 2.3.1 Plant oils . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14 2.3.2 Monomers . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 14 3 Biobased plastics. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 16 3.1 Introduction. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 16 3.2 Biobased / partially biobased. . . . . . . . . . . . . . . . . . . . . . . 19 3.3 Modified natural polymers . . . . . . . . . . . . . . . . . . . . . . . . . 21 3.3.1 Thermoplastic starch . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 21 3.3.2 Cellulose-based plastics . . . . . . . . . . . . . . . . . . . . . . . . . . 22 3.3.3 Natural rubber and thermoplastic elastomers. . . . . . . . . 24 3.3.4 Lignin-based plastics. . . . . . . . . . . . . . . . . . . . . . . . . . . . . 26 3.3.5 Protein-based plastics . . . . . . . . . . . . . . . . . . . . . . . . . . . . 26 3.3.6 PHA. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 27 3.4 Polymers synthesised from biobased monomers. . . . . . . 30 3.4.1 Biobased polyesters . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 30 3.4.2 Biobased polyamides . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 36 3.4.3 Biobased polyurethane. . . . . . . . . . . . . . . . . . . . . . . . . . . . 38 3.4.4 Biobased polyacrylates. . . . . . . . . . . . . . . . . . . . . . . . . . . . 39 3.4.5 Biobased polyolefins. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 39 3.4.6 Biobased thermoset resins. . . . . . . . . . . . . . . . . . . . . . . . . 41 3.4.7 Other biobased plastics . . . . . . . . . . . . . . . . . . . . . . . . . . . 42 3.4.8 Bioplastics from waste. . . . . . . . . . . . . . . . . . . . . . . . . . . . 43 4 Methods of processing plastics . . . . . . . . . . . . . . . . . . . . 46 4.1 Introduction. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 46 4.2 Compounding. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 46 4.3 Further processing . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 47 4.3.1 Extrusion . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 47

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4.3.2 Blown film extrusion. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 48 4.3.3 Injection moulding. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 49 4.3.4 Blow moulding. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 50 4.3.5 Thermoforming. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 52 4.3.6 Foams. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 52 4.3.7 Casting. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 54 4.3.8 Other plastic processing methods. . . . . . . . . . . . . . . . . . . 54 4.3.9 Joining plastic together . . . . . . . . . . . . . . . . . . . . . . . . . . . 55

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5 Applications . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 56 5.1 Packaging. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 56 5.2 Catering. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 58 5.3 Horticulture and agriculture. . . . . . . . . . . . . . . . . . . . . . . . 59 5.4 Medicine and personal care. . . . . . . . . . . . . . . . . . . . . . . . 61 5.5 Consumer electronics. . . . . . . . . . . . . . . . . . . . . . . . . . . . . 62 5.6 Automobile manufacture . . . . . . . . . . . . . . . . . . . . . . . . . . 63 5.7 Textiles. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 65 5.8 Other. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 66

9 9.1 9.2 9.3

Legal and regulatory background. . . . . . . . . . . . . . . . . . 82 Standards and certification regarding “compostability”. . 82 The Packaging Ordinance. . . . . . . . . . . . . . . . . . . . . . . . . . 83 Standards and certification regarding “Biobased”. . . . . . 83

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Suggested further reading. . . . . . . . . . . . . . . . . . . . . . . . 86

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Sources of information on the Internet. . . . . . . . . . . . . . 88

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List of references. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 90

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Potential and perspectives. . . . . . . . . . . . . . . . . . . . . . . . 78 Further developments. . . . . . . . . . . . . . . . . . . . . . . . . . . . . 78 Do we in fact have enough agricultural land?. . . . . . . . . . 79

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The market. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 74

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6 End of Life / Disposal / Closed loops. . . . . . . . . . . . . . . . 68 6.1 Recycling. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 68 6.1.1 Material recycling. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 68 6.1.2 Chemical recycling . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 69 6.2 Composting. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 69 6.3 Energy recovery or thermal recycling . . . . . . . . . . . . . . . . 70 6.4 Land fill . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 71 6.5 Closed loops. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 72

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13 Index . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 96

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BIOPLASTIC WHAT IS IT EXACTLY?

1.1 FUNDAMENTALS Polymers (from the Greek Poly = many, meros = particles) are long-chain molecules (macromolecules), that can also be branched.

The molecules, entangled like cotton wool, produce a solid material that can be reshaped - plastic. The precursors of polymers are monomers (mono = one) and oligomers (oligo = few) 1

Plastics are organic polymers1 which can be processed in various different ways. Their technical properties, such as formability, hardness, elasticity, rigidity, heat resistance and chemical resistance, can be varied across a wide range by selecting the correct raw materials, manufacturing process, and additives.

Plastics are lighter and more economic than many other materials. For these reasons, plus their extreme versatility and excellent processability, they are the material of choice in many industrial and commercial applications [1, 2]. Since the widespread availability of petroleum at the beginning of the 20th century most traditional plastics have been produced using petroleum.

The statistics (2010 figures) are impressive: the plastics industry employs more than 1.6 million people in Western Europe and turns over some 300 billion Euros per annum. Out of the approximately 230 million tonnes of plastics produced annually worldwide about one quarter comes from Europe. Its applications are not only in packaging (40%), construction materials (20%), but plastic is also needed in automobile production (7%) and furniture manufacture, as well as in the electronics industry http://bioplasticsmagazine.com/e and in the manufacture of domestic equipment of all types [3].

Accordingly the demand for plastics continues to grow – for example demand in 1976 stood at 50 million tonnes worldwide, and by 2015 is expected to reach 330 million tonnes.

But plastic isn‘t simply plastic. Whilst thermoset resins remain permanently in a rigid state after hardening, thermoplastics can be melted again, or reshaped by the application of heat.

These thermoplastics are the most commonly used and hold an 80% share of the market. Another group of plastics covers the ductile plastics or thermoplastic elastomers [1].

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6 | 1 BIOPLASTIC - WHAT IS IT EXACTLY?

1 FROM RENEWABLE RESOURCES bio-PE, bio-PP bio-PA cellulose-acetate bio-polyisoprene bio-PET, bio-PTT

PLA PHA (PHB...)

TPS Celluloseregenerates

PE-LD, PE-HD PP, PA, PS PVC, EVOH, oxo-fragmentable blends

Co-Polyester (PBAT), Polycaprolacton, PVA, ...

BIODEGRADABLE / COMPOSTABLE

NOT DEGRADABLE

no bioplastics

FROM FOSSIL RAW MATERIALS

Fig. 1.1: Biobased and biodegradable plastics (based on Endres [4])

1.2 BIOPLASTICS

The widely used term “bioplastics� is not totally unambiguous and covers several groups of plastics. These on the one hand are biobased plastics (made from renewable resources) and on the other hand biodegradable plastics. Many bioplastics fall into both categories (top right in Fig. 1.1).

The main focus in biobased plastics is the origin of the basic raw materials, i.e. renewable resources, in contrast to petroleum, which is a limited resource. Renewable resources are often referred to as RRs (or RRM for Renewable Raw Materials).

Biodegradable plastics are classified according to the way in om/en/books/bioplastics.php which they can be disposed of. These plastics are accessible to micro-organisms as a source of nutrition and energy, and the metabolic structure of the organisms means that they can break the material down into carbon dioxide (CO2), water and biomass (see also chapter 1.2.2).

Biobased plastics may or may not be biodegradable plastics.

Biodegradable plastics may or may not be produced from renewable resources.

In fact it is a general misconception that biobased plastics are automatically also biodegradable, and vice versa.

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1.2 BIOPLASTICS | 7

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1.2.1 BIOBASED PLASTICS Plastics basically consist of macromolecules that in general are made up of carbon (C), hydrogen (H) and other components such as oxygen, nitrogen etc. If the origin of the carbon/carbonates is from a fossil resource (petroleum, natural gas, coal) we talk about conventional, traditional or petroleum-based plastics.

The carbon component in biobased plastics comes from current, rapidly renewable, resources. These may be fruits from various plants, or also so-called remnants such as stalks, leaves, etc.

Even trash disposal routes such as communal waste water can be rich in current carbon substances so that they are basically suitable as a resource for biobased plastics. (cf. chapter. 3.3.6).

The biobased plastics will be dealt with in detail more in this publication.

1.2.2 BIODEGRADABLE PLASTICS

2 Protozoa are single cell organisms with a cell nucleus, such as paramecia, amoeba etc.

A substance or a material is biodegradable if it is broken down by micro-organisms such as bacteria, protozoa2, fungi, or enzymes. The micro-organisms use the substances as nutrients or a source of energy. The remainder of the broken down substance consists of carbon dioxide (CO2), water and mineral salts of other elements present (mineralisation), plus biomass [5].

A difference is made between aerobic degradation in the presence of oxygen, as is the case in a compost heap, and anaerobic degradation. In anaerobic degradation there is no oxygen present. In bio-gas plants for example, this type of degradation leads to the production of methane that can be captured in a controlled way and used for energy generation. The conversion of organic waste into bio-gas is also often referred to as anaerobic digestion (AD) [6].

In connection with biodegradability the term compostability is often used, and there is a clear difference made between industrial composting [7] and composting in a domestic back garden (home compostable) [8]. The key difference within the general description of biodegradability is the question of time. Biodegradable substances are compostable if their total breakdown in the compost heap is achieved in a comparably short time. In industrial composting the time to achieve total breakdown is only about 45 to 90 days. In industrial composting the breakdown is also carried out under optimum conditions such as average temperatures of 58-65°C, relative humidity of about 98% and an optimum population of micro-organisms.

8 | 1 BIOPLASTIC - WHAT IS IT EXACTLY?

1 Even plastics themselves can, where their chemical composition allows, be biologically broken down, composted or used to produce bio-gas using the methods above. Some biodegradable plastics must first be broken down by hydrolysis or oxidation into smaller components before the micro-organisms can metabolise the material.

There are relevant standards and legal requirements in existence covering the biodegrability of plastics and their certification (including EN 13432, ASTM D6400) (cf chapter 9).

A special case of biodegradability is breakdown of materials within the human body. So-called resorbable plastic materials have been used for many years as surgical thread. Bone screws made from resorbable polyesters can spare many patients a second operation because the screws degrade within the body and after being broken down are ejected by the metabolism.

Biodegradable plastics are not necessarily made from renewable resources in order to be completely biologically degradable.

Plastics such as polybutylene adipate-terephthalate (PBAT) an aromatic aliphatic co-polyester that is used, for instance, for film and refuse sacks, is made 100% from petroleum but is nevertheless fully biodegradable. Other examples are polybutylene succinate (PBS) or polybutylene succinate adipate (PBSA) etc.

The first successes in producing such biodegradable yet petroleum-based plastics using at least some renewable resources have already been recorded [9, 10].

The term “biodegradable” is here to be clearly separated from the materials used now and then in the packaging industry and which are stated to be “oxo- biodegradable” or “oxo-degradable” [2]. These materials, made from traditional plastics (often PE, or at times PP or PET) are restructured generally by using an additive containing metal which is often claimed to make them “biodegradable” or even “compostable”. Such claims are misleading insofar as it has not been demonstrated that the product meets the requirements of EN 13432 or EN 14495. In the case of plastic packaging these claims are legally required to be substantiated in line with EN 13432 (or ASTM D 6400). None of the “oxo-degradable” materials known at this time meet these requirements.

Instead of complete biological breakdown the product simply breaks down into extremely small particles. As a result associations such as European Bioplastics distance themselves from oxo-(bio)degradable plastics. In legal decisions numerous examples of misleading claims have been evidenced [11, 12].

1.2 BIOPLASTICS | 9

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1.3 BIOBASED PLASTICS - WHY?

3 This is equally true of natural gas and coal, albeit based on a different time scale and amount. When we here refer to petroleum we include all sources of fossil energy.

Above all there are two important points that support the concept of producing plastics from renewable resources rather than petroleum . On the one hand there is a limited availability of petroleum3, and on the other hand most experts are agreed that the burning of products from fossil resources is a contributor to global warming and a potentially hazardous climate change.

The price of oil The fact that petroleum is a limited resource and has become much more expensive in recent years can be clearly seen, and not just at every filling station. Between 1998 and 2007 the price of oil increased around sevenfold, hitting 146 US Dollars per barrel (159 litres) in July 2008 (Fig. 1.2). Even if the price of oil fell back to about 45 Dollars as a result of the economic crisis in the autumn of 2008 we can reasonably assume that in the medium term it will increase again, and go above the 2007 level. When this book went to press (in early 2012) the price of oil (Brent) was around 110 Dollars.

At the present time plastics account for only about 4 to 7 percent of total petroleum usage. This effectively means that replacing petroleum-based plastics with those made from renewable resources cannot save the world from a severe shortage of oil. The plastics industry can, however, by using biobased plastics, make itself less dependent on the increasing and fluctuating cost of oil because those renewable resources that are most easy to obtain, when used in sustainable production, will represent an unlimited source of carbon when oil is no longer available.

Climate The fact that the combustion of fossil fuels such as petroleum, natural gas and coal involves an irreversible release of CO2, and that this CO2 has, as a so-called greenhouse gas, an influence on our climate and thus on global warming, is a generally accepted reality [4].

Products that are made from (today short term) renewable resources can, when burned, emit an amount of CO2 into the atmosphere equivalent to the plants from which they are produced, as a maximum, and which they have absorbed from the atmosphere via photosynthesis during growing. This also applies to

10 | 1 BIOPLASTIC - WHAT IS IT EXACTLY?

1 150 125 100 75 50 25 0

2004 2005 2006 2007 2008 2009 2010 2011

biofuels and wood pellets as well as to biobased plastics. In this respect biobased plastics are “climate neutral�. However, since there is a requirement for further energy use during harvesting, and processing of the plastic, as well as for transport, (in part from fossil sources) this statement about climate neutrality is not strictly correct. Here individual cases should be assessed by way of closer examination such as by carrying out an eco-balance or life cycle analysis (LCA).

US-$ per Barrel

Fig. 1.2: The development in oil prices (Brent) (Source of data: heizoel24.de)

1.3 BIOBASED PLASTICS - WHY? | 11

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RENEWABLE RESOURCES 2.1 INTRODUCTION Biobased plastics can be produced from a wide range of plant-based raw materials. On the one hand natural polymers, i.e. macromolecules that occur naturally in plants etc., are used.

And on the other hand smaller molecules, such as sugar, disaccharides and fatty acids (plant oils), are used as the basic raw materials in the production of bioplastics. Such renewable resources can be obtained, modified and processed into biobased plastics.

2.2 NATURAL POLYMERS By natural polymers (biopolymers) we mean polymers synthesised by any living organism. These may be, for example, polysaccharides, proteins or lignin, that act as energy reserves or have a structural function for the cells or the whole organism [2].

The term “biopolymers” (polymers which occur in nature) must be clearly differentiated from the term “bioplastics” from which products can be made in the same way as they can be made from conventional plastics.

Many of the naturally occurring biopolymers briefly summarised below (but certainly not all of them) can be used for the manufacture of biobased plastics.

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2.2.1 POLYSACCHARIDES (CARBOHYDRATES)

Among the most important biopoymers are the polysacchahttp://bioplasticsmagazine.com/e rides (multiple or many sugars). α-polysaccharides for instance fill an energy storage role in starch. Starch in turn consists of amylose and amylopectin, two natural polymers. β-polysaccharides act as structural substances, for example in cellulose, the main component in the cell walls of plants. Not quite so important is chitin (found for example in the exoskeleton of many insects or animals with shells) which belongs to the β-polysaccharide group. Chitosan is produced from chitin and is also found in many types of fungi. A blend of polysaccharides and fructose molecules is inulin, which is found in many plants and acts as an energy reserve.

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2.2.2 PROTEINS

2

Proteins are biopolymers built up of amino acids. They exist in all living creatures and serve to move substances around the body, or as a substance that provides a structural framework, as signal sources, or as catalysts.

Proteins include casein from the milk of mammals. Gluten is a mixture of different proteins that is found in the seeds of grain crops. Collagen is a structural protein of the connective tissue (e.g. skin, teeth, sinews, ligaments or bones) in many higher life forms. Collagen is the main basic material for the manufacture of gelatine.

2.2.3 LIGNIN Lignin is a 3-dimensional cross-linked aromatic macromolecule. The solid, colourless substance is contained in the cell walls of plants and causes the lignification (turning into wood) of grasses, shrubs, bushes and trees etc. Alongside cellulose, lignin is the most common organic substance on earth. As a byproduct of the pulp and paper industry around 50 million tonnes of lignin are produced each year [13]. The majority of it is burned for energy recovery.

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2.2.4 NATURAL RUBBER Natural rubber is an elastic biopolymer from plants - mainly latex from specific trees. Alongside the rubber tree latex is also obtained from other trees such as bulletwood (Manilkara bidentata) or gutta percha. Natural rubber is the most imporant raw material used in the production of vulcanised rubber.

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An interesting group of biopolymers are the polyhydroxyalkanoom/en/books/bioplastics.php ates - polyesters that are formed in certain micro-organisms as an energy reserve (cf. chapter 3.3.6).

Other complex groups of natural polymers, such as nucleic acid etc. shall not get closer examination at this point.

2.2 NATURAL POLYMERS | 13

2.3 OTHER BIOGENIC MATERIALS

2

2.3.1 PLANT OILS In addition to the natural polymers mentioned above plant oils have a very important role to play as a source of carbonates for the production of biobased plastics.

Vegetable oils are fats and fatty oils that are obtained from oilseed plants and the fruits of so-called oil plants. Alongside their use in human and animal food, as lubricants or energy sources, a number of vegetable oils can also be used as raw material for the manufacture of bioplastics.

Those principally used are soya oil, castor oil, palm oil and rapeseed oil, as well as sunflower oil, linseed oil and a few others. The vegetable oils used to produce bioplastics, and the type of bioplastic they can produce, will be covered in chapter 3.

2.3.2 MONOMERS In addition to the substances listed above there is also a range of monomers and dimers that can be used for the production of biobased plastics.

Alongside polysaccharides these are monosaccharides (sugar) such as glucose and fructose (both C6H12O6) or disaccharides such as sucrose (C12H22O11). Sucrose contains glucose and fructose units in a ratio of 1:1 joined by a glycosidic bond [2].

Certain bivalent alcohols which can also be used (partly) in the production of biobased plastics are able themselves to be produced from renewable raw materials For a few years now biobased 1,3-propanediol has been sold as bio-PDO, and 1,4-butanediol will soon be marketed as bioBDO, produced from renewable resources such as maize starch for example [14, 15].

The range of so-called biobased chemical building blocks is not only increasing considerably in its application in the manufacture of plastics. An important area, which has been a significant object of research in recent times is succinic acid (C4H6O4), which can also be made by fermentation, using starch and various oligosaccharides.

An important monomer used for PLA, one of the most significant bioplastics on the market today, is lactic acid (Details in chapter 3.4.1).

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2.3 OTHER BIOGENIC MATERIALS | 15

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The world’s most commonly produced plastic is polyethylene.

Its ethylene monomer is today mainly obtained by way of steam cracking carbonates such as naphtha or also ethane, propane and liquefied gas. By dehydrating bio-ethanol, based on sugar cane, a biobased ethylene for the production of bio-polyethylene can be obtained (see chapter 3.4.5).

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Fig. 3.1: Doll made from celluloid (Picture: Holger Ellgaard)

BIOBASED PLASTICS 3.1 INTRODUCTION

Plastics have not always been produced from fossil materials such as petroleum. Quite the contrary – the first plastics were already bio-based. In the early years of the history of plastic the first plastic materials were used as an alternative to costly and scarce raw materials, and were obtained via the chemical transformation of natural materials [1, 16]. These valuable and scarce raw materials were, for example, towards the end of the 19th century, mother of pearl, tortoiseshell, horn or ivory, but also amber, coral, lapis lazuli and ebony [2].

Celluloid is regarded as the world’s first “plastic”, discovered in 1855 by the Englishman Alexander Parkes and initially sold under the name Parkesine [17]. In 1869 the Hyatt brothers (USA) opened their first factory for the production of celluloid, a thermoplastic material. Thus began the age of plastics. The publication at the time of a prize competition gave the legendary boost to the development of plastics that could be used in place of costly ivory for the production of billiard balls. Celluloid made from cellulose nitrate and camphor set the pace and was quickly adopted for other applications such as Picturegraphic film, decorative manufactured goods, spectacle frames, combs, table-tennis balls and other products [1]. A significant disadvantage of celluloid was its easy combustibility, http://bioplasticsmagazine.com/e especially when the moisture content of film material was reduced over an extended period of time.

In about 1923 the mass production of cellulose hydrate (cellophane) began.

Known under the original trade name of Cellophan, and marketed by Hoechst AG, it is a crystal clear, crispy film and one of the oldest plastics that came into direct contact with foodstuffs [2].

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Another, less combustible cellulose based material, cellulose acetate, has slowly replaced cellophane in certain applications [18].

Cellulose acetate (CA) or cellulose triacetate (CTA) are obtained from cellulose in a reaction with acetic acid and even today still (or once again) have a significant place in the bioplastics market (cf. chapter 3.3.2) Casein is the protein component in the milk of higher mammals that is not found in whey. From the end of the 19th century until the 1930s casein was one of the raw materials for the plastic called galalith, which was used among other things for making buttons, personal decorative items, and also as an insulation material in electrical installations [2].

During the first decade of the 20th century Henry Ford in the USA tried to find non-food applications for excess agricultural production. He tried initially with, amongst other things, wheat and soya, and one of the first series applications was a starter box for the 1915 Model T Ford, produced with an asbestos fibre reinforced synthetic resin made from wheat gluten. Following this Ford attempted several applications for products made from soya oil, such as paints and lacquers, a substitute for rubber, and for the production of glycerine used in shock-absorbers. Liquefied soya proteins were placed in a formaldehyde bath to create fibres for upholstered parts. Differom/en/books/bioplastics.php ent plastic products were produced from soya meal – a by-product after the extraction of soya oil – by reaction with formaldehyde. Soya meal plastic was used by Ford for a steadily increasing number of vehicle parts, such as glove-box lids, gear knobs, horn buttons, throttle pedals, distributor covers, internal linings, steering wheels, instrument panels, and later for a prototype trunk lid (Fig. 3.4) [19].

Fig. 3.2: Decorative comb 1920/1930 and hair pin 1920/1950 made from celluloid (Pictures: Kunststoffmuseums-Verein e.V., Düsseldorf)

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Fig. 3.3: Buttons 1920/1940 made from casein (Picture: KunststoffmuseumsVerein e.V., Düsseldorf) 3.1 INTRODUCTION | 17

3 Fig. 3.4: Henry Ford hitting his car with an axe. The trunk lid is a soya plastic reinforced with hemp (Picture: The Henry Ford Museum)

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These early “biobased plastics” were soon forgotten in the age of the petroleum boom. The availability of petroleum in huge quantities and at a low cost ensured that “modern” plastics such as PMMA (Plexiglas®, 1930), and later polyamides like PA 6.6 (Nylon®) PA 6 (Perlon®), polystyrene and PTFE (Teflon®) (1930 – 1950) were the centre of attention. Finally, from 1956, the industry mastered the large scale production of today’s mass-market plastics polyethylene (PE) and later polypropylene (PP). With the industrial production of plastics there followed, over the years, the development of various techniques for the processing of these plastics [1] (see also chapter 4).

Only from 1980, and increasing at the turn of the century, did bioplastics become once again a focus of research and development. The principal interest at that time was biodegradability and compostability. Meantime it became clear that compostability is only a sensible option where it offers some additional benefit, and where it is not just another method of disposal.

Of major significance, especially in view of limited petroleum availability and price development, as well as global warming, is the production of plastics from renewable resources (i.e. biobased plastics). Fundamentally biobased plastics can be produced from numerous plant-based raw materials.

As mentioned above, whilst about 100 years ago cellulosebased materials were the first plastics, they were soon outpaced by petroleum polymers. The renaissance of bioplastics began with plastics based on starch (starch blends and also starch raw materials). The reasons were, and are, the relatively low and increasingly interesting price, good availability of the raw materials, and the excellent biodegradability of the plastic as possible unique features (see chapter 1.2.2)..

Starch, after hydraulic cracking into glucose (previously also dextrose) is also used as a raw material in fermentation processes. In this way new bioplastics such as PLA and PHA are produced. Sugar is also the raw material for the latest generation

3.2 BIOBASED / PARTIALLY BIOBASED In recent years a whole range of biobased plastics has been developed and successfully launched onto the market. These are 100% biobased plastics like PLA, PHA or bio-PE, as well as partially biobased plastics. The latter can be plastics that are produced from various raw materials (monomers, oligomers) and which (so far) have not all been able to be produced from renewable resources, or they are blends of biobased and petroleumbased plastics.

Examples of the first group of partially biobased plastics are certain bio-polyamides (see chapter 3.4.2). A whole range of producers offer polyamide 6.10 where the dicarbonic acid (via sebacic acid) required for its production is produced from castor oil or soya oil, the diamine, however, is of petrochemical origin. Effectively there is a bio-based content of around 63% (cf definition of “biobased content” below). Another example is polyethylene terephthalate (PET, known for its use in beverage bottles). A large producer of soft drinks in 2010 launched a bottle where the PET had been made from bio-based monoethylene glycol (obtained from sugar cane molasses) and conventional terephthalic acid.

At the beginning of 2011 the other soft drink giant hit back with a 100% biobased PET bottle. This supplier claimed that they had cracked the code and could produce terephthalic acid from renewable resources.

Blends of biobased and petrochemical plastics are, for example, mixtures of PLA (100% bio) and PBAT (polybutylene adipate terephthalate, a petroleum based but compostable copolyester).

Such blends, including those made from other plastics, can be used in a wide range of applications thanks to their mechanical, 3.2 BIOBASED / PARTIALLY BIOBASED | 19

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of bioplastics including the biobased polyolefins PE (and soon to come is PP), PVC, as well as the partially biobased polyester PET, which however are all not biodegradable. As so-called “drop in” polymers their properties are totally identical to the fossil based variants that dominate the market today. Optimising the products for improved technical performance is therefore not required, which significantly reduces the time taken for technical and economic acceptance by the market. A great future is forecast for these materials, particularly long term, when the infeed is successfully switched by biorefinery to non-food raw materials such as wood or cellulose rich plant residue (see also chapter 3.4.8).

Further details will be discussed in the following chapters.

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thermal and other properties, and can be almost tailor-made for the application in question. If biobased and biodegradable plastics (like PLA) are “blended” with plastics made from petrochemicals and that are not biodegradable, such as PLA/PC (Polycarbonate), then their biodegradability is of course lost.

Even when it is the declared aim of many companies and researchers to produce plastics totally based on renewable resources, any approaches in the direction of partially biobased plastics are a step in the right direction (see also chapter 3.4).

Definition: biobased content When stating the percentage of biobased material in a plastic the experts have different approaches. On the one hand only the carbon percentage is looked at. The percentage of fossil raw material and/or “young” carbon can be determined by the radiocarbon method. An American standard (ASTM D6866) gives precise steps on how to do this. For example here the monoethylene glycol mentioned above contributes 20% and the terephthalic acid 80% of the carbon atoms, based on the following formula: + n C8H6O4 n C2H6O2  (C10H8O4)n + n(2 H2O) (monoethylene glycol + terephthalic acid = PET + water) The other approach takes into account the biomass content as a percentage by weight. In this method the monoethylene glycol accounts for about 30 % of the biobased content of bio-PET. Both approaches have their supporters and their opponents [20] depending on one’s point of view. Hence both are important and necessary.

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3.3 MODIFIED NATURAL POLYMERS

To produce thermoplastic starch (TPS) starch grains are destructured by an extrusion process [2, 4]. Starch consists of two components, the branched polymerised amylopectin, which is the principal component and which encases the unbranched amylose [1]. In order to destructure the starch it must be subjected to sufficient mechanical energy and heat in the presence of so-called plasticisers or softening agents.

The best softener for starch is water at a concentration of 45%. Other softeners are glycerine, sorbitol, etc. During destructuring the granular structure and the original crystallinity (a left-handed double helix) of the natural starch is destroyed [21]. TPS with a starch content of over 90% (plus water etc.) can in general be used only for the production of foamed loose fill packaging chips. To produce TPS material that can be processed on film blowers, injection moulding machines or used in the extrusion blow moulding process, the starch is blended with other bioplastics such as PBAT [22].

Thermoplastic starch with suitable softening agents, or blends with PBAT can, for example, be very successfully blown to form film (chapter 4.3.2). The preferred application is plastic pouches, shopping bags and sacks that can also be used for disposal of biological refuse. Foamed TPS is used as a loose fill material (Fig. 3.6) to protect fragile products during transport.

Because thermoplastic starch is hydrophilic and very brittle it is compounded with other bioplastics for many applications to create waterproof or water repellent blends. The other components of the blend may be, for example, polyester, polyesteramide, polyurethane or polyvinyl alcohol.

Starch blends or compounds can be individually developed and produced for various applications in the plastics industry.

They can be processed to produce injection moulded items, film, thermoformable sheet for deep-drawn products, or coatings. Examples of some of these applications are seen in shopping bags, yoghurt pots, single-serve beverage containers, plant pots, cutlery, nappy liners, and coated paper and card [2].

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3.3.1 THERMOPLASTIC STARCH

Fig. 3.5: Granulate of destructured and complexed starch [1]

Fig. 3.6: TPS loose fill to protect fragile products (picture: Novamont)

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FIBRES CELLULOSE

CELLULOSE

CELLULOSEDERIVATIVES

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REGENERATED CELLULOSE

Fig.3.7: Cellulose-based polymer materials (Picture: according to [4])

FIBRERS

3.3.2

FILMS

CELULOSE -ESTER

CELULOSE -ETHER

CELLULOSE-BASED PLASTICS

Cellulose is the principal component of cell walls in all higher forms of plant life, at varying percentages. It is therefore the most common organic compound and also the most common polysaccharide (multi-sugar). Cellulose is unbranched and consists of several hundred (up to ten thousand) glucose molecules (in a glucosidic bond) or cellobiose units. The cellulose molecules bind together with higher structures that often have a static function as tear-resistant fibres in plants [2, 5 23].

In cotton wool the cellulose content reaches about 95%, in hardwood from 40 to 75%, and in soft woods it is between 30 to 50%.

Cellulose is, in terms of quantity, the most significant renewable raw material resource – globally about 1.3 billion tonnes are obtained each year for technical applications. However chemical processes are required to remove undesirable contaminants such as lignin and pentoses from the cellulose fibres. An important end product is cellulose pulp which is mainly used to produce paper and cardboard, but is also used for textiles [1].

Furthermore cellulose can be used industrially in the form of cellulose regenerates and cellulose derivatives (Fig. 3.7).

Cellulose regenerate If cellulose is chemically dissolved and newly restructured in the form of fibres or film it is known as a cellulose regenerate.

The most well-known members of this group of materials are viscose, viscose silk, rayon or artificial silk, and a few more in the area of fibres and textiles. In the field of film are cellulose hydrate and also cellulose film, known by the original brand name of Cellophane [4].

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Fig. 3.8: Cellophane – a crystal clear cellulose product [1]

Fig. 3.9: Artificial silk (Picture: iStock)

Cellulose derivatives With regard to industrial use cellulose derivatives (including biobased plastics) play an important role. They are classified into two main groups - cellulose ethers and cellulose esters [4].

By the etherification of cellulose with alcohols various cellulose ethers can be produced, such as carboxymethyl cellulose (CMC), methyl cellulose (MC), and others, that are used as glues (carpet adhesive, tile adhesive), cleaning and washing products, pharmaceutical and cosmetic products, and many more.

Cellulose esters here have a considerably higher importance for the plastics industry. The first thermoplastic material was celluloid, produced from 75% cellulose nitrate (obtained from nitric acid and cellulose) and 25% camphor.

Basically cellulose esters occur by the esterification of cellulose with organic acids. The most important cellulose esters from a technical point of view are cellulose acetate (CA with acetic acid), cellulose propionate (CP

Fig. 3.10: Swiss army knife, grip made from celluloseacetobutyrate

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with propionic acid) and cellulose butyrate (CB with butanoic acid). Mixed polymerisates, such as cellulose acetate propionate (CAP) can also be formed. One of the most well-known applications of cellulose aceto butyrate (CAB) is the moulded handle on the Swiss army penknife. To improve the thermoplastic processability and the mechanical performance in use, softening agents (3 to 35%) are as a rule added to the cellulose acetates [2, 5].

3.3.3 NATURAL RUBBER AND THERMOPLASTIC ELASTOMERS Fig. 3.11: Transparent dice made from cellulose acetate

4 Indian: „the tree that weeps“ from cao = tree, and ochu = tears

A very popular “relative” of plastics is rubber. Other associated terms are natural latex and elastomers. Even though about 60% of the world demand for rubber is today produced from petrochemicals (synthetic rubbers, mainly from styrene and butadiene), the trend is moving back to the use of materials from renewable resources.

By natural rubber (caoutchouk4) we mean polymers that are based on plant products, and principally latex. In nature this latex sap runs from damaged areas of the tree‘s bark and so acts as a protective substance for the tree by closing off damaged areas and preventing bacterial contamination. In sustainable cultivated plantations the sap is obtained by making deliberate slits in the bark (Fig. 3.12).

By vulcanising the crude latex with sulphur rubber is produced [2]. During vulcanisation the long chain rubber molecules are cross-linked by the sulphur. The rubber is thus no longer able to be reshaped or softened by melting, but becomes extremely elastic thanks to this process [24].

In addition to rubber, which has been known as a biological material for many decades, there are thehttp://bioplasticsmagazine.com/e so-called thermoplastic elastomers (TPE). These plastics, which are also very elastic, are not cross-linked and so can be remelted (thermoplastics).

There is a whole range of biobased or partially biobased types available.

An important group here are the thermoplastic polyurethanes (TPU, or occasionally TPE-U). Their range of applications goes from the soles of shoes, and other shoe parts, to film and the soft component of hard-soft bonded parts such as tooth-brush

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handles. For details of biobased polyurethanes see chapter 3.4.3.

Thermoplastic ether-ester elastomer (TPCET) with hard sections produced from petrochemical polybutylene terephthalate (PBT) and soft sections that contain a polyether produced using biobased 1,3 propanediol (cf. chapter 2.3.2), is suitable for technical applications such as airbag covers in passenger cars. A version exhibited in 2010 consists of 35% by weight of renewable raw material (Fig. 5.22) [25].

A 100% biobased TPE is a block copolymer (polyether block amide) that in 2010 was presented for, among other things, ski boots. The TPE material consists of 100% biobased polyamide 11 (cf chapter 3.4.2) and biobased polyether [26].

The first biobased EPDM (ethylene propylene diene monomer) for the production of EPDM rubber was presented at the end of 2011 in Germany and Brazil. Here the ethylene component is produced from Brazilian bioethanol [82].

Another thermoplastic elastomer produced totally from renewable resources and which was successfully launched in 2009, is based on 100% wheat proteins. The material is also biodegradable, which is not the case with those previously mentioned (Fig. 3.16) [27].

Fig. 3.12: Latex harvesting from a rubber tree (Hevea brasiliensis) in Cameroon (Picture: PRA)

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Fig. 3.13: Walking shoes with partially biobased polyurethane (TPU) (Picture: Bayer)

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Fig. 3.14: Loudspeaker housing made from a lignin-based bioplastic (Picture: Tecnaro)

Fig. 3.15: Biodegradable urn made from ligninbased plastic (Picture: Alento)

3.3.4 LIGNIN-BASED PLASTICS The most well-known bioplastic based on lignin (chapter 2.2.3) is sold under the name of “liquid wood� [13, 28] and is easy to process in injection moulding machines (chapter 4.3.3). This bioplastic is also sold containing natural fibres (flax, hemp) to increase its strength.

As a reinforcing component in partially biobased polyurethane (with polyols based on soya), lignin at a percentage by weight of 5% offers a significant improvement in rigidity and distension [29]. Thus there are at the moment numerous different research projects being carried out with the aim of using lignin in the plastics industry.

3.3.5 PROTEIN-BASED PLASTICS Another group of bioplastics can be produced from animal or plant proteins (see also chapter 2.2.2). Casein is one of the bioplastics made from animal protein, and was already a significant player at the beginning of the age of plastics (see chapter 3.1.). To make a casein plastic the basic casein, obtained from skimmed milk and plasticised, is processed to form a cross-linked plastic by the action of formaldehyde and the removal of water. In this context the term casein-formaldehyde is commonly used. Because of their comparably low technical characteristics casein plastics are used today only in small niche markets [4].

A different type of protein-based plastic is gelatine. It is used, in addition to the well-known applications, as a nutritional sup-

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Fig. 3.16: Thermoplastic elastomer made from 100% wheat protein (Picture: Tereos Syral)

plement and also as a binding agent or capsule for pharmaceutical tablets [4]. In the majority of cases gelatine is produced from collagen (see chapter 2.2.2).

Some new developments in the field of bioplastics based on plant proteins are concerned, for example, with extrusion compounding of soya protein with water and glycerine, or the production of formaldehyde and soya based resins. Because of their limited performance profile, bioplastics based on plant proteins are not currently found on the market on an industrial scale [4].

An example of a thermoplastic elastomer that is based on 100% wheat protein, and is also biodegradable, was presented in 2009 and won an award (Fig. 3.16).

Fig. 3.17: Storage of energy reserves (Picture: iStock)

3.3.6 PHA Starch and other substances that supply carbonates can also be converted into bioplastics by fermentation and the action of micro-organisms.

Examples are the polyhydroxy alkanoates (PHA) or the polyhydroxy fatty acids, a family of polyesters.

As in many mammals, including humans, that hold energy reserves in the form of body fat there are also bacteria that hold intracellular reserves 3.3 MODIFIED NATURAL POLYMERS | 27

3 Fig. 3.18: Electron microscope image of bacteria with stored PHA particles (Picture: Metabolix)

of polyhydroxy alkanoates [4]. Here the micro-organisms store a particularly high level of energy reserves (up to 80% of their own body weight) for when their sources of nutrition become scarce. By “farming” this type of bacteria, and feeding them on sugar or starch (mostly from maize), or at times on plant oils or other nutrients rich in carbonates, it is possible to obtain PHS‘s on an industrial scale.

PHAs are optically active, aliphatic polyesters with a structure as shown in Fig. 3.19.

Fig. 3.19: Structural form of PHA (general) [4]

If the rest (R) is a simple methyl group CH3, we talk about polyhydroxy butanoic acid or polyhydroxy butyrate (PHB). Where R = C2H5 polyhydroxy valerate (PHV) is produced, where R = C3H7 polyhydroxy hexanoate (PHH) is produced, and where R = C4H9 polyhydroxy octanoate (PHO) is produced etc. [5].

Today those most economically interesting are PHB or copolymers such as PHBV (poly-3-hydroxy butyrate-covalerate), PHBH (poly-3-hydroxy butyrate-co-3-hydroxyhexanoate) or PHBHV, which in the 1990s was used for a shampoo bottle (Fig 3.21) in markets including Germany and the USA, but later disappeared from the market.

Processable bioplastics made from polyhydroxy alkanoates are generally obtained by removing the biopolymer from the bacterial cell material, and cleaning and compounding it.

PHAs are mainly film and injection moulding grades (Fig. 3.20) and are now increasingly available as extrusion and blow moulding grades. A Japanese company in 2009 showed a particle foam (similar to Styrofoam®) and made from PHBH [30].

A special feature of polyhydroxy alkanoate is the fact that it can be composted in an industrial composter or biogas installation, and also on a home compost heap, or in the soil or in the sea just as rapidly, and is 100% biodegraded.

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Research activity is also going on in the field of transgenic plants such as switchgrass (Panicum virgatum L.), a prairie grass from North America, or tobacco plants that form PHB as an energy reserve [1, 31, 32]. Here PHB could be obtained directly without going along the detour involving bacteria.

Efforts currently being made in New Zealand, for example, go even further. Here they are carrying out experiments based on municipal waste water (Fig. 3.22). This waste water contains some not inconsiderable amounts of available carbonates, for example from small particles of food waste from dishwashers. Since in purification plants the waste water is in any case clarified by the action of micro-organisms such as bacteria it seems logical to check whether micro-organisms that produce PHA can become particularly “well-fed� and whether the polymer could ultimately be harvested. The first trial results are very promising [33]. It will however probably take a number of years before this solution takes on a real commercial significance.

Fig. 3.20: Bathroom accessories injection moulded from PHBV (Picture: Design Ideas)

control

3 months in compost

9 months in compost

Fig. 3.21: shampoo bottle made of PHBHV (Reproduced with permission [108])

Fig. 3.22: Research in New Zealand - PHA taken from communal waste water (Picture: Scion) 3.3 MODIFIED NATURAL POLYMERS | 29

3.4 BIOBASED POLYMERS SYNTHESISED FROM BIOBASED MONOMERS 3.4.1 BIOBASED POLYESTERS

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PLA

Fig. 3.23: Processing steps for the generation of polylactide materials and parts made from PLA (according to [4])

In this group of materials PLA (polylactide, polylactic acid) is today’s most important bioplastic on the market [4]. PLA is based on lactic acid, a natural acid, is mainly produced by fermentation of sugar or starch with the help of micro-organisms.

Lactic acid comes in two isomer forms, i.e. as laevorotatory D(-) lactic acid and as dextrorotary L(+)lactic acid.

Two lactic acid molecules form a circular lactide molecule which, depending on its composition, can be a D-D-lactide, an LL-lactide or a meso-lactide (having one D and one L molecule).

The chemist makes use of this variability. During polymerisation the chemist combines the lactides such that the PLA plastic obtained has the characteristics that he desires. The purity of the infeed material is an important factor in successful polymerisation and thus for the economic success of the process, because so far the cleaning of the lactic acid produced by the fermentation has been relatively costly [1].

The world’s first large PLA production unit with a capacity of 140,000 tonnes per annum began production in the USA in 2002. Industrial PLA production facilities can now be found in the Netherlands, Japan and China. In Guben/Germany a 500 t/a pilot plant started operation in 2011.

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CONDITIONING OF SUBSTRATES

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FERMENTATION MICROORGANISMS

ISOLATION

INOCULATION LACTIC ACID PLA MATERIAL

PRODUCT

PROCESSING

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BLENDING/ ADDITIVES

SYNTHESIS

POLYMERIZATION

LACTIDE

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PLA is, as it exits the reactor, not an easily processed plastic. Hence, as is usual with most plastics, raw PLA polymer is adapted to specific applications by compounding (cf chapter 4.2) with suitable additives or by copolymerisation or blended with other plastics (bioplastics or traditional plastics).

Advantages of the polylactide plastic are its high level of rigidity, transparency of the film, cups and pots, as well as its thermoplasticity and good processing performance on existing equipment in the plastics converting industry. Nevertheless PLA has some disadvantages: as its softening point is around 60°C the material is only to a limited extent suitable for the manufacture of cups for hot drinks [1]. Modified PLA types can be produced by the use of certein additives or by a combinations of L- and D- lactides (stereocomplexing), which then have the required morphology for use at higher temperatures [34]. A second characteristic of PLA together with other bioplastics is its low water vapour barrier. Whilst this characteristic would make it unsuitable, for example, for the production of bottles, its ability to “breathe” is an advantage in the packaging of bread or vegetables.

Transparent PLA is very similar to conventional mass produced plastics, not only in its properties but it can also be processed on existing machinery without modification. PLA and PLA-blends are available in granulate form, and in various grades, for use by plasom/en/books/bioplastics.php tics converters in the manufacture of film, moulded parts, drinks containers, cups, bottles and other everyday items [1]. In addition to short life packaging film or deep drawn products (e.g. beverage or yoghurt pots, fruit, vegetable and meat trays) the material also has great potential for use in the manufacture of durable items.

Examples here are casings for mobile phones, possibly reinforced with natural fibres, desktop accessories, lipstick tubes, and lots more. Even in the automotive industry we are seeing the first series application of plastics based on PLA. Some Japanese car manufacturers have developed their own blends which they use to produce dashboards [35], door tread plates, etc.

Fig. 3.24: Transparent PLA film for packaging vegetables

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Fibres spun from PLA are even used for textile applications.

On the market we can already find all kinds of nonwovens and textiles from articles of clothing through children’s shoes to car seat covers.

Furthermore there are lucrative special markets, for example in medical and pharmaceutical applications where PLA has been successfully used for some time. From screws etc. that are slowly resorbed into the body, to nails, implants and plates made from PLA or PLA copolymers, the parts are used to hold broken bones in place as they heal. The PLA is broken down within the body and ejected by the human metabolism, so saving the patient the problem of a second surgery to remove the previously implanted parts. PLA has also been used for a long time for resorbable sutures and plasters containing active substances [1].

Polylactides and their copolymers or blends are rapidly, slowly, or not at all biodegradable, depending very much on their composition. Whilst pure poly-L-lactide takes years to degrade, PLA made from D- und L-lactides degrades in a few weeks. Blends of PLA with non-biodegradable plastics, such as PLA/PC, are simply not biodegradable. This shows clearly the special diversity of this bioplastic, that can be used in a form that rapidly biodegrades or, if required, in a functional form that can be used for years [1].

PET PET, since the second half of the 20th century, has been a mass-produced plastic. A real boom began in 1975 with its use by the big North American soft drinks companies to make “easyto-grip” and “unbreakable” beverage bottles.

PET is a thermoplastic polyester that is produced by polycondensation of monoethylene glycol (or ethylene glycol, a bivalent alcohol, a diol) and terephthalic acid or dimethyl terephthalate.

Since 2010 the first beverage bottles have been supplied made from partially biobased PET [37]. The monoethylene glycol (about 30% by weight) is obtained from sugar cane molasses.

The terephthalic acid is in this application still produced from petrochemical resources. At about the same time a Japanese automobile group also announced that it was producing partially biobased PET [38].

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3 Fig. 3.25: Desktop accessories made from PLA

Fig. 3.28: Baby’s shoes made from a PLA/PET blended fabric and soles made from a soft PLA compound [36]

Fig. 3.27: Lower dashboard panel made from a PLA blend (Picture: Mazda [35])

Fig. 3.26: CARGO PlantLove™ lipstick tube made from Ingeo (PLA) (Picture: CARGO)

Fig. 3.29: Gattinoni Obama Dress 100% Ingeo (Picture: Gattinoni)

Fig. 3.30: Seat cover made from 100% biobased PLA fibres (Picture: Mazda [35])

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At the beginning of 2011 another of the soft drinks giants announced the launch of 100% biobased PET bottle. The production of terephthalic acid as the second component of PET (and other plastics) using renewable resources had been regarded as too elaborate and costly. Now, however, there are apparently clear routes to the economic production of biobased terephthalic acid [39].

One approach is to produce using naturally occurring carbohydrates such as fructose (C6H12O6), by catalysis with 2,5-dimethyl furan [62] and then to produce paraxylene (p-Xylol or 1,4-dimethylbenzene) again using the benefit of catalysts. This is the prime ingredient for the production of terephthalic acid. Another route is to obatin paraxylol from 2,5-dimethyl furan and ethylene in a cycloaddition reaction (a reaction forming ring molecules) described in a US patent [40]. Other synthesis routes go from isobutanol / isobutane or muconic acid, and PTA can also be obtained thermochemically in various stages (the syngas route) [22].

Regardless of whether PET is partially or totally produced from renewable resources, chemically the material is identical to conventional PET and can thus be recycled together with conventional PET.

Fig. 3.31: Partially biobased PET (Picture: Coca-Cola) Fig. 3.32: 100% biobased PET (Picture: PepsiCo)

PEF A 100% biobased alternative to PET could be Polyethylene Furanoate (PEF). 2,5 Furan Dicarboxylic acid (FDCA) can be polymerized with ethylene glycol to produce Polyethylene Furanoate. A technology was developed in the Nethelands to produce FDCA from biomass [106].

Fig: 3.33: 2,5-dimethyl furan (left), paraxylol (centre), terephthalic acid (right)

CH3

O

OH

O

OH

O2 H3C

O

CH3

-H2O CH3

34 | 3 BIOBASED PLASTICS

Polytrimethylterephthalate (PTT), which is also partially biobased, is certainly not as well known, or has the same market importance as PET. PTT has however, as a partially biobased plastic, been on the market much longer than (partially) biobased PET Similarly to PET, PTT is also produced using terephthalic acid (until now made from petrochemical resources, in future also to be biobased?), or dimethyl terephthalate and a diol. In this case it is a biobased 1,3 propanediol, also known as bio-PDO (cf chapter 2.3.2).

PTT was first launched onto the market mainly in the form of spun fibres and textiles. Because they are particularly soft and yet can bear heavy wear the principal area of application was for domestic carpets and carpets for the automobile industry.

But PTT is also suitable for injection moulding applications and quite comparable to polybutylene terephthalate (PBT). With a high quality surface finish, and low shrink and deformation performance, the material is ideal for, amongst other things, electrical and electronic components such as plugs and housings, or also for air breather outlets on car instrument panels [41, 42].

3

PTT

Fig. 3.34: Clothes made from PTT fibres (Picture: DuPont)

Fig. 3.35: Carpet made from PTT fibres (Picture: DuPont)

3.4 POLYMERS FROM SYNTHESISED BIOBASED MONOMERS | 35

3

Biobased polysuccinates

Fig. 3.36: Packaging made from polybutylene succinate (PBS)

Other bio-polyesters are, for example, polybutylene succinate (PBS), a 100% biodegradable bioplastic that is produced from butanediol (in future e.g. bio-BDO) and succinic acid, and which can also be produced in a biobased form (see chapter 2.3.2).

With polybutylene succinate adipate (PBSA), in addition to the succinic acid, adipic acid is polymerised within the compound. This plastic too can be biobased to a greater or less degree depending on the origin of the monomer.

Other biobased polyesters Other (fully or partially) biobased polyesters are polybutylene terephthalate (PBT) made from terephthalic acid or terephthalic acid methyl ester, and biobased butanediol (bio-BDO). PBT is seen as a “technical brother” of PET, which is preferred for use as packaging.

As has been mentioned in chapter 1.2.1, the first successes have been achieved, including production of a partially biobased version of the very succesful 100% biodegradable plastic PBAT (polybutylene adipate terephthalate) which is at times produced from renewable resources [9].

3.4.2 BIOBASED POLYAMIDES

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Polyamides are plastics that are particularly suitable for fibres and technical applications. The most well known examples, which caused a sensation in the first half of the last century, are Nylon und Perlon. Polyamides today are used for demanding injection moulding applications, extruded products, hollow http://bioplasticsmagazine.com/e articles and textiles for the manufacture of clothing, decorative materials and technical fabrics. They are characterised by a combination of methylene groups (-CH2-) and amide groups (-NH-CO-). Basically polyamides are divided into two groups.

A-B polyamides (such as PA 6, PA 11 or PA 12) consist of a single repeating unit.

you can order th

[NH−(CH2)X−CO]n where (X+1) = 6, 11 or 12, (respectively X = 5, 10 or 11)On the other hand AA/BB polyamides (such as PA 6.4, PA 6.6 or 36 | 3 BIOBASED PLASTICS

PA 6.10, today mostly referred to in a shorter form as PA 64 or PA 66 or PA 610) are distinguished by having two repeating units.

Here the figures in the type nomenclature give the number of carbon atoms in each repeating unit (X and Y+2): in the example PA 6.10 X=6 and Y+2=10 [43, 44, 45, 46].

Bio-polyamides are totally or partially biobased depending on whether the dicarbonic acid, the diamine, or both are produced from renewable resources [47].

An economically important dicarbonic acid for the production of bio-polyamides is sebacic acid [HOOC(CH2)8COOH] or C10H18O4, which can be obtained from the castor oil plant (Fig. 3.37). Using this monomer it is possible to produce partially biobased polyamides such as PA 4.10 or PA 6.10.

Here the “10”-component is the biobased part.

Both partially biobased PA 4.10 and also PA 6.10 are commercially available.

If both monomer types are produced from biobased raw materials thern 100% biobased polyamides can be produced. An example is PA 5.10, which until now has been just a laboratory product.

Here the “10”-component can be produced as before based on sebacic acid, and the“5”-component in this case produced using biobased diamine 1,5 diaminopentane (or pentamethylenediamine) om/en/books/bioplastics.php [H2N(CH2)5NH2] or C5H14N2, which by microbial break-up of protein from the natural occurring amino acid lysine [2].

A further example is PA 10.10, which is also commercially available. Here too the first “10”-component is biobased. The base material 1,10 diaminodecane (or decamethylene diamine) [H2N(CH2)10NH2] or C10H24N2 can also be obtained from the castor oil plant, so that PA 10.10 is also 100% biobased.

w Sample

3

[NH−(CH2)X−NH−CO−(CH2)Y−CO]n

Fig. 3.37: Castor oil (photo: fotalia (seed), Thielen (plant))

the book at

Fig. 3.38: Wall fixing plugs made from partially biobased PA 6.10 (Picture: Philipp Thielen)

3.4 POLYMERS FROM SYNTHESISED BIOBASED MONOMERS | 37

3

An example of the first group of polyamides mentioned above is completely biobased PA 11, which has already been on the market for more than 60 years. It can only be made from castor oil, is totally biobased and is suitable, thanks to its special chemical and general resistance, for biofuel pipework and other components.

In addition to those mentioned here there are still some more biobased polyamides [47].

Fig. 3.39: Fuel connector nipples made from 100% biobased PA 11 (Picture: Arkema)

Fig. 3.40: Car seat made from soya foam (Picture: Ford Motor Company)

38 | 3 BIOBASED PLASTICS

3.4.3 BIOBASED POLYURETHANE Polyurethanes are produced by a reaction between polyols and diisocyanates and can be hard and brittle, elastic, foamed or compact. Because polyols can be obtained from plant oils such as castor oil or soya oil there are already a large number of partially biobased polyurethanes on the market.

So-called thermoplastic polyurethane, TPU, as a member of the elastomer group, has already been mentioned in chapter 3.3.3.

Another important group of polyurethanes comes in the form of foams used in automobile manufacture. As a pioneer in this field one of the big North American automobile groups has, for a number of years, been using polyurethane foam where the polyol is produced based on soya. The first foams (soy foams) from this automobile manufacturer were “only” 5 wt% and made from renewable resources but work is going on apace to increase the biobased element of the polyol. Areas of application are seats, head-rests etc. Other car manufacturers – and their suppliers – use, in addition to soya oil, plant oils based on castor oil, rapeseed oil, or palm oil to manufacture polyols. A Japanese manufacturer of PU foam presented at the K‘2007 plastics exhibition a polyurethane foam where the polyol was 100% based on castor oil. With a 70% polyol content and 30% isocyanate content this means a 70% content in the finished polyurethane coming from renewable resources [48].

Acrylic plastics include, as an example, PMMA (polymethyl methacrylate) which is also known as Plexiglas® or acrylic glass. Scientists from the University of Duisburg Essen have discovered an enzyme that allows them to produce a precursor of methylmethacrylate (MMA) which in turn serves as a monomer for the production of PMMA and is based on a biotechnical process using natural raw materials such as sugar, alcohol or fatty acids [49].

Furthermore there are currently efforts being made to be able to use a biobased version of the platform chemical (platform chemicals are standard chemicals that can be used for a variety of purposes) 3-hydroxypropionic acid for the production of further raw materials to make acrylic plastics [50]. Such raw materials include, for instance, acrylic acid, methacrylic acid, acrylic nitrile, acrylic amide etc. Plastics that can be produced using these types of raw materials include, amongst others, ABS (acrylonitrile butadiene styrene, see also chapter 3.4.7), a hard, viscoplastic that is used to make the world’s best known play building bricks.

3

3.4.4 BIOBASED POLYACRYLATES

Fig. 3.41: Trophy made from PMMA (acrylic glass, not biobased in this case)

3.4.5 BIOBASED POLYOLEFINS Among the most important and most commonly used plastics are polyolefins (polyethylene PE and polypropylene PP). They are easily recognised by the fact that their density is less than 1 g/cm³ - i.e. they float in water. Both PE and PP can be produced from renewable resources [51].

Fig. 3.42: Building brick made from ABS (here not biobased) (Picture: Stilfehler)

Bio-polyethylene Polyethylene (PE) is the simplest and at the same time most common plastic with a global capacity of 80 million tonnes (2008 [51]). There are numerous possible applications, going from film (pouches, bags, shrink film) through blow-moulded hollow articles such as shampoo bottles and petrol canisters, to barrels, automobile fuel tanks, or injection moulded parts such as tubes and profile sections.

3.4 POLYMERS FROM SYNTHESISED BIOBASED MONOMERS | 39

3

H H | | — C — C — | | H H n Fig. 3.43: Structure of the simplest plastic: polyethylene

Fig. 3.44: Shampoo bottle made from bio-PE (Picture: Braskem)

40 | 3 BIOBASED PLASTICS

PE has a structure [CH2-CH2]n which means that the backbone of the polymer chain consists of carbon atoms with a hydrogen atom attached to each, hence the molecular chain can also be branched.

Depending on whether, and to what extent, the molecular chains are branched different basic types can be made. PE-HD (previously known as HDPE) is weakly branched and exhibits a higher density (hence the name PE-HD: high density polyethylene). In contrast PE-LD (LDPE) is strongly branched and of a lower density, and PE-LLD is a linear polyethylene that has fewer and shorter branches.

In addition there are also very high density types known as PEHMW or even PE-UHMW, ultra-high molecular weight PE, that among other things can be spun to make fibres, for example, for ballistic textiles (bullet-proof vests etc.).

Polyethylene can be produced petrochemically by polymerisation of ethylene gas. This gas is itself produced in Europe and Asia by steam cracking of various carbonates, mainly naphta. In the USA, Canada and the Middle East ethane, propane and liquefied gas are also used.

Another way in which the monomer ethylene can be produced is by dehydration of ethanol. This method was used at the beginning of large scale PE production in the first half of the 20th century, before the availability of petrochemically produced ethylene gas [2].

Having in mind the production of plastics from renewable resources this process has once again attracted interest. For instance in Brazil bio-ethanol has been produced for many years from sugar cane by a fermentation process. This bio-ethanol can now be used for the production of ethylene and hence bio-polyethylene.

In Brazil there is now significant production capacity.

Bio-polypropylene

3

Biobased polypropylene can, like bio-PE, be produced from bio-ethanol but the process is much more complex. Polypropylene (PP) [C3-H6]n is considerably younger than PE and is used in numerous technical applications. Global production in 2008 was in the order of 44 million tonnes [51].

CH3 H | | — C — C — | | H H n

Basically PP can be processed using all of the methods outlined for PE. Also of interest is the biaxial stretching of film to make BO-PP (biaxial oriented PP). In this way the surface area is significantly increased and by orienting the molecules the film is given improved mechanical properties.

To produce bio-PP there are several ways of obtaining the propylene monomer C3H6 from renewable resources [52]. A large Brazilian producer of polyolefins has announced the start-up in 2013 of a bio-PP plant but without diclosing details about which method will be used to produce the plastic [53].

Fig. 3.45: Carpet and bottles made from bioPP (Picture: Braskem)

3.4.6 BIOBASED THERMOSET RESINS Thermoset resins are cross-linked plastics that cannot be remelted. They are often strengthened by the use of reinforcing fibres such as fibreglass, carbon fibres, aramid fibres (Kevlar®, Twaron®) and less frequently with natural fibres. The most important thermoset resins are epoxy resins and unsaturated polyester resins.

Unsaturated polyester resins Unsaturated polester resins (UP) are known for example in boat building and the repair of damaged bodywork on a car. They are also usually reinforced with (or filled with), for example, fi-

3.4 POLYMERS FROM SYNTHESISED BIOBASED MONOMERS | 41

3 Fig. 3.46: Speedboat Chase 700iBR made from partially biobased UP resin (Picture: Ashland)

breglass in the form of sheet moulding compounds (SMC) or bulk moulding compounds (BMC) and principally used in the construction of new vehicles.

Polyester resins are condensation products from bivalent or polyvalent alcohols (e. g. glycols or glycerine) and dicarbonic acids [2], and as described above (see also chapters 2.3.2, 3.4) can be produced from renewable resources. Today there is a whole range of partially biobased UP resins on the market [54, 55].

Epoxy resins

Another thermoset resin which is used in boat building is epoxy resin, and is also known for its use in air travel and space travel, racing cars or wind energy plants, in particular for lightweight construction with carbon fibre reinforcement. It is used in tennis racquets, racing motor cycles and many other technically demanding applications. A further important area of application is in two-component adhesives..

The possible ways of producing expoxy resins are very different and complex. Often epichlorhydrin with bisphenol A (also a bivalent alcohol, a diol) is converted to epoxy resin, however health and safety concerns about bisphenol A have led recently to alternatives being sought. Epichlorhydrin is easy to obtain from biobased glycerine, a by-product from bio-diesel production [56]. It is already being produced on an industrial scale.

An alternative way to produce 100%http://bioplasticsmagazine.com/e biobased epoxy resin (without bisphenol A) was presented at the beginning of 2011 [57]. The researchers produced a polyamine from grape seed oil which is then used as a hardener for a reaction with epoxidized linseed oil.

Preview S

you can order th

3.4.7 OTHER BIOBASED PLASTICS As has been clearly shown there are many plastics that can be fully or partially biobased because there is a wealth of monomers, platform chemicals or other substances, the so-called chemical building blocks, which can be obtained from renew42 | 3 BIOBASED PLASTICS

3.4.8 BIOPLASTICS FROM WASTE

A much-discussed topic is the potential conflict involving the possible use of food or animal feed resources for the production of bioenergy or biofuel. And even though the requirement would be a lot smaller, this applies also to the industrial use of materials from renewable resources for bioplastics. In this connection it is often argued that the use of plants that should produce food or animal feed is only a transitional phase and that scientists are working under extreme pressure to be able to produce bioplastics from waste streams or even from domestic rubbish.

Against this is the argument that food producing plants have been so optimised for agriculture over decades, if not centuries, that their usable carbonate content has reached a maximum. A target for optimum resource use should be to use fertile land as efficiently as possible, regardless of whether the cultivated land could be used for food production or not [59].

A more important question in this regard is whether there is in om/en/books/bioplastics.php total enough land available for the production of plants in order on the one hand to feed the world population and on the other hand for the generation of energy and production of raw materials.

Because this discussion could fill another book it will not be analysed in depth here. The author is convinced, however, that there is enough land available but where its use and distribution is one of the great challenges of our time. This means [59]: “Even if an increasing percentage of agricultural land is used for energy production and the production of raw materials there are plenty of possibilities to extent the total amount of agricultural land, and

w Sample the book at

3.4 POLYMERS FROM SYNTHESISED BIOBASED MONOMERS | 43

3

able resources. These are, for example, the bio-PDO and bioBDO diols, monoethylene glycol, sebacic acid, succinic acid, terephthalic acid and many more.

Every step taken to replace fossil-based carbonates with “young” carbonates from renewable resources is a step in the right direction.

This certainly includes the advance made by a Thai supplier of ABS (acrylonitrile butadiene styrene, a technical plastic), who has been successful in producing the butadiene component, albeit so far only 25%, from renewable resources. This results in a biobased percentage of 4% in the ABS. Ongoing research is currently aiming at 8% [58], possibly with reference to the acrylonitrile component too.

3 Fig. 3.47: Bioplastic products based on potato waste (Picture: Rodenburg)

44 | 3 BIOBASED PLASTICS

even more possibilities to raise the level of productivity�.

Despite this there are currently efforts being made, with a number of successes, to be able to produce plastic from waste and domestic waste.

An example can be seen in the Netherlands where there is a flourishing potato industry (for chips / french fries). When peeling and slicing the potatoes on an industrial scale there is, in addition to the peels and other waste, a large amount of water used during the processes.

This process water, like the peels and other waste, has a high percentage of useable starch.

So there are now companies in the Netherlands that produce plastics from the starch so obtained [60]. Similar approaches to the use of process water containing starch and associated waste are also established in several other parts of the world.

In chapter 3.3.6 efforts made in New Zealand were already mentioned. Polyhydroxy alkanoate is obtained from municipal waste water systems .

A few years ago a large brandowner took the used frying oil from his production line for shaped potato crisps and used it as a food source for PHA producing micro-organisms. Thus old frying fat became a high quality plastic material [22, 61].

3 | 45

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4

METHODS OF PROCESSING PLASTICS 4.1 INTRODUCTION

4

plastic granules conveying direction

melt exit

barrel

screw

Fig. 4.1: Sketch of a plastifying unit

In this book the principal focus is put on thermoplastics, i.e. plastics that become soft again (plasticised) at elevated temperatures and so can be remelted and given new shapes. In most cases the melting, or more correctly plastification, is done in screw feed units (see sketch in Fig. 4.1). In this way, using a machine comparable to a domestic mincer, in addition to external electrical heating additional heat is usually applied through dissipation. The raw plastic in granulate form is loaded into the machine via a cone-shaped funnel and conveyed by the rotating screw of the plastifying unit (Fig. 4.2). It is melted, homogenised and then delivered to further processing.

4.2 COMPOUNDING

Fig. 4.2: Plastifying screws for plastics (picture: Kautex Maschinenbau)

46 | 4 METHODS OF PROCESSING PLASTICS

A polymer only becomes a “plastic” if it can be converted into a product using conventional processes. Like most “conventional plastics”, most bioplastics emerging from the reactor as “raw plastics” cannot as a rule be converted to end products. They must be correctly adapted to the specific application by compounding. Compounding means preparing for use, and describes the enhancing process that raw plastics go through, being blended with certain additives (e.g. fillers or other additives) to optimise their properties for the planned application [2]. Such additives can be processing aids, UV stabilisers, impact resistance modifiers, plasticisers, colour pigments and many more. The objective is to adapt the mechanical or thermal properties

4.3 FURTHER PROCESSING The compounds, ready for further processing, are now converted, in a wide range of processes, into components or finished products. To do this in most cases existing plastic processing machines and installations can be used. It is generally only a matter of adjusting the process parameters such as temperature, pressure etc. Hygroscopic materials, i.e. those that tend to absorb moisture from the atmospheric air, must be pre-dried using appropriate equipment.

Even though basically most existing plants and machinery are suitable for processing bioplastics, it is possible to achieve a high standard of performance by optimising machines or machine sections, such as plastifiers, hot-runners nozzles etc. For instance improvements can be achieved in gentle plastifying and at the same time increased output.

4

of the plastic to suit the end product and to make the plastic processable.

Compounding is often done in a twin screw extruder specially built for this purpose, (more on extruders in chapter 4.3.1) and where the components can be particularly thoroughly mixed together and homogenised. The raw materials can be compounded in the form of granulate, powder or even liquids. The process consists of certain well-defined stages, or phases: plasticising of the polymer, mixing with the additives, homogenising, degassing, pressurising, ejection through a nozzle, (where necessary also passing through a filter stage to remove any foreign material or contaminants) and finally cooling of the emerging melt and pelletising [63, 64].

Fig. 4.3: Principle of a co-rotating twin screw extruder (picture: Coperion)

4.3.1 EXTRUSION Extrusion (from the Latin extrudere = push out, drive out) means a continuous plastifying, conveying and pushing out of a thermoplastic material through a specifically shaped die. In this way con4.3 FURTHER PROCESSING | 47

4 Fig. 4.4: Blown film extrusion (picture: Der Grßne Punkt – Duales System Deutschland GmbH)

tinuous products such as piping, engineering profiles, film or plates can be produced.

The machines used, the extruders, consist normally of a material infeed, a plastifying unit where one or two screws are used, and, where needed, additional stages such as degassing, the profiling nozzle, a cooling section and a discharge outfeed for the finished product. Most extruders also incorporate a saw to cut the extruded product into manageable lengths.

Not only finished products such as pipework, engineering profiles, plates etc, can be extruded, but also semi-finished products. Such products may be, for example, thicker film that can be further processed by thermoforming (chapter 4.3.5).

A way of improving the mechanical properties of extruded film is stretching immediately after extrusion (in-line stretching). The molecules are oriented such that the tensile strength and rigidity are increased. Stretching can be in one direction (e.g. lateral stretching) or in both lateral and longitudinal directions. An example here is biaxially oriented PLA film (BoPLA) [65].

By adding a foaming agent a foam extrudate can also be produced (chapter 4.3.6).

And finally extruders may also be part of an installation for complex processes such as film blowing (chapter 4.3.2) or extrusion blow moulding (chapter 4.3.4).

4.3.2 BLOWN FILM EXTRUSION

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In order to blow thin film an extruder is combined with a ring nozzle. The plastified mass of material is, between the extruder and the nozzle, formed into a tube and forced upwards through the nozzle. There the tube-shaped melt is air blown to a much higher diameter than the original, and pulled upwards at a higher speed. It is not only the biaxial pull but also the moment ofhttp://bioplasticsmagazine.com/e cooling that determine the thickness of the film. The tube is laid flat and then rolled up either as a tubular film or slit along the side to make a flat film. It is not unusual to see this type of film blowing installation as a 10 metre high tower.

By installing several extruders for different types of plastic, multi-layer film can be produced. Each plastic takes on a specific role, such as rigidity, a barrier function, the ability to be welded etc.

Products made from blown film are, for example, packaging, rubbish sacks and bags for biological waste,

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48 | 4 METHODS OF PROCESSING PLASTICS

hygienic foil for nappies, mailing pouches, disposable gloves and shopping bags [1].

4.3.3 INJECTION MOULDING

4

Almost all sizes and shapes of plastic parts can be made by injection moulding. A screw plastifier softens the plastic as the screw moves slowly back during the melt process to enable a shot of melted plastic to build up in front of the screw tip. Once the quantity needed for one shot is reached the screw moves forward and presses the melt through the pre-heated nozzle and under pressure through the feed channel to the cavity of the cold

Fig. 4.6: Injection moulding machine (picture: Ferromatik Milacron)

w Sample cooling

the book at mould

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heating

screw

granules plasticizing drive injection, cooling with after-pressure

demoulding

Fig. 4.5: The injection moulding process (picture: according to www.fenster-wiki.de)

4.3 FURTHER PROCESSING | 49

mould, the so-called “tool”. The plastic now cools down in the tool and is ejected as a finished moulded part [1].

The possible applications for injection moulding are almost endless. Some examples are ball-point pens, rulers and other office accessories, disposable cutlery, garden furniture, car bumpers, beverage cases, knobs and handles, small mechanical parts, and lots more.

4

4.3.4 BLOW MOULDING

Fig. 4.9: Preforms and bottles (from left to right): PLA, PP, PET) (Picture: Plastic Technologies [68])

Plastic hollow articles are mostly produced by blow moulding.

There are various processes available but the most commonly used are extrusion blow moulding and stretch blow moulding.

[66].

In extrusion blow moulding the thermoplastic melt is produced in an extruder from where it is ejected vertically downwards through an annular die to create a soft tubular “parison”.

A mould consisting of two vertical halves (the blow mould) is closed around the freely suspended parison and squeezes this at both ends (top and bottom). Now the parison is inflated through a blowpin or needle and pressed against the cold walls of the blow mould tool, where it cools and becomes harder, taking on the shape of the mould. The blow mould is opened and the plastic hollow article is removed. Finally the remnants (known as the flash) cut from the squeezed ends are removed Typical areas of application for this process are bottles (shampoo, ketchup, detergents etc.), jerricans, canisters, drums, barrels, tanks and also games and sports equipment such as kayaks or kid’s ride-on cars, plus lots more.

An early extrusion blow moulded packaging made from bioplastic was a shampoo bottle made from a polyhydroxyalkanoate (PHBHV) in the 1990s. The latest examples are a small bottles made from bio-PE for a probiotic drink from a major supplier of dairy products [67].

A different process to the versatile extrusion blow moulding technique is stretch blow moulding which is used almost exclusively for the manufacture of (beverage) bottles. Here a small preform that resembles a test tube with a screw thread at the neck is first injection moulded.

50 | 4 METHODS OF PROCESSING PLASTICS

1. Plasticizing and preparation of melt

Fig: 4.7: Extrusion blow moulding (Picture from [66])

4

2. Forming of a tube-like melt parison

3: Shaping of final article in the mould by inflating the parison with air Flash

Flash Deflashing 4. Postprocessing

Fig. 4.8: Stretch blow moulds (Picture: KHS Corpoplast)

4.3 FURTHER PROCESSING | 51

4

This preform is then, in a separate machine, heated in a radiation oven, following which it is sealed in a mould and stretched laterally by a stretching rod. Its diameter is also stretched, by high pressure air. This biaxial stretching of the molecules gives the plastic a high degree of rigidity and firmness such that thinwalled containers can be produced.

A bioplastic that is ideally suited for this process is PLA. 4.3.5 THERMOFORMING Fig. 4.10: Stretch blow moulded PLA bottles

By thermoforming (previously known as hot forming, deep drawing or vacuum deep drawing) we refer to the production of three dimensional moulded parts from semi-finished flat plastic material (film, plate etc.) [2, 69]. Heat and high pressure air are used, and sometimes a vacuum, plus where required a mould to help stamp the three dimensional shape.

The film is drawn from a large roll or in-line directly from an extruder and fed to the automatic moulding unit where it is taken through in an indexed motion. At a heating station the film is heated up by radiation on one or both sides. In the tool station the film is held firm by clamping frames. Where necessary a stamping tool or an initial blast of air is used to roughly shape the desired contour. Then high pressure air is applied on one side and a vacuum is drawn on the opposite side in order to bring the film swiftly and firmly against the cold surface of the mould.

The cooled film, now rigid again, is ejected from the mould tool and at the next station is punched out of the remaining flat film.

Typical applications are chocolate box inserts, blister packaging, yoghurt or margarine tubs, drinking cups, meat trays, clamshell packs, and other similar packaging applications. Larger parts such as sand boxes and kids’ paddling pools, and through

52 | 4 METHODS OF PROCESSING PLASTICS

Fig: 4.11: Thermoforming (picture: CUSTOMPARTNET)

Clamp Plastic Sheet

Heaters

4

Finished Part

Form

Molded Part

Vacuum Pump

to technical parts for cars, can be made using the thermoforming process.

4.3.6 FOAMS With the objective of making moulded parts that are particularly light, that have good heat and noise insulation, or good mechanical damping, or simply to save on material, plastics can be foamed. Here we differentiate between open cell structures (e.g. a sponge) and closed cell structures (e.g. for heat insulation).

During foaming the porous structure is generated by a physical, chemical or mechanical process. In physical foaming low boiling point liquids (e.g. volatile organic compounds) are added to the plastic which vaporise during the polymerisation process and so form the typical gas bubbles. Chemical foaming is similar

Fig. 4.12: Thermoformed packaging made from PLA (picture: DuPont (left) Ilip (right)) 4.3 FURTHER PROCESSING | 53

4

Fig. 4.13: Foamed trays top: PLA (picture: Coopbox group) bottom: PLA blend (picture: FKuR)

to the use of baking soda. Chemical foaming agents are often solids that are added to the plastic and which break down at higher temperatures, releasing gases [70]. And in mechanical foaming gas is simply blown into the plastic melt as it is being agitated (cf. whipped cream).

Now we find different plastic products depending on the way that they are processed. Using an extruder, panels or profile sections with a consistent cell structure or possibly with a foamed core and compact outer faces (integral foam) are produced [1]. Extruded foam panels or film can also be further processed by thermoforming. An example is seen in foamed PLA meat trays.

With polyurethane the foam structure is created by elimination of water (water vapour, steam) through the reaction of polyol with isocyanate (see also chapter 3.4.3).

Another interesting area is particle foams. Known as EPS (expanded polystyrene, and also under the trade name StyroporÂŽ (BASF)), particle foams made from PLA (E-PLA) have been successful in penetrating the market [71]. Here tiny spheres are loaded with a foaming agent (e.g. pentane or sometimes CO2). A mould is filled to a certain volume with these spheres and then heated. The spheres grow larger and melt together as a result of the high pressure.

4.3.7 CASTING There are also certain bioplastics that cannot be processed, as discussed above, in a thermoplastic process. Film made from cellulose acetate cannot be extruded or blown, but has to be cast.

54 | 4 METHODS OF PROCESSING PLASTICS

In addition to the processes described briefly here there is a whole range of other plastic processes but which so far have been rarely used or used very specifically for bioplastics.

These include rotational moulding for the production of very large and thick walled hollow parts such as large underground tanks.

In calendering a plastic compound is fed into a large rolling mill and pressed into a film format. Other processes include, for example, die casting, injection-compression moulding etc..

4

4.3.8 OTHER PLASTIC PROCESSING METHODS

Fig. 4.14: PLA particle foam (picture: Synbra)

4.3.9 JOINING PLASTIC TOGETHER Semi-finished products or component parts made from thermoplastics can be fixed together in various ways (joining). The use of adhesives must be one of the most well-known joining processes. Whilst polyolefins, because of their low polarity can only be stuck together after additional processing, such as flame treatment or corona discharge, most other plastics can be successfully glued. Under the influence of pressure and heat thermoplastics can also be welded together. Thus tubes and piping can be joined, or containers, packaging, shopping bags, carrier bags, pouches and sacks can be so produced. The principal of plastics processing based on welding is widely used in many variants and the use of a film welding device to pack food in PE film pouches has, for instance, already found its way into many homes [1].

Plastic parts can, using the right constructive design, also be screwed or riveted. Lockable or unlockable snap connections, already an ideal solution for plastics, are also very popular.

4.3 FURTHER PROCESSING | 55

5

APPLICATIONS Bioplastics are used today in numerous applications. Chapter 7 examines the recent market statistics in some detail.

5.1 PACKAGING

5

Alongside simple, foamed packaging chips (loose fill) based on starch (Fig. 5.1), which can also be coloured and used as children’s toys, there is now a huge number of packaging items made from bioplastics. Technically almost everything can be done: bioplastics can be blown as film or multilayer film, or extruded as flat film. They can be thermoformed and are able to be printed, glued and converted into packaging components in numerous ways. In short: packaging manufacturers and packers can process bioplastics on almost all of their usual machines with no problems [1].

Established packaging applications for bioplastics are shopping bags, which also have a secondary use as a bag to collect compostable kitchen and garden waste. Further applications are thermoformed inserts for chocolate boxes, trays for fruit, vegetables, meat and eggs (also foamed), tubs for dairy produce, margarine and sandwich spread, bottles, nets or pouches for fruit and vegetables. Blister packs, where the film is closely formed to follow the profile of the packaged product, can also be produced. For use in the cosmetics business there are jars and tubes. Packaging materials made from bioplastics with barrier properties, impenetrable to odours and with good performance on the machines are available now, and are also the subject of continuous ongoing development [1].

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Fig. 5.1: Starch based packaging flakes (picture: above [1], right Thielen)

56 | 5 APPLICATIONSS

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Fig. 5.2. Compostable bags are suitable for use for collecting bio-waste (picture: BASF)

Fig. 5.3: Foamed PLA tray (picture: Coopbox Italia)

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Fig. 5.4: PLA yoghurt pot (picture: Philipp Thielen)

Fig. 5.5: Fruit net made from PLA-blend (picture: FKuR) 5.1 PACKAGING | 57

5

Coating of paper and cardboard laminates with bioplastics leads to new packaging with good moisture and fat or oil resistance [72].

In the USA a mineral water bottle made from PLA bioplastic was launched as early as 2005. This was followed by a range of other bottles for water, milk and juice in North America, Europe, Australia, New Zealand and other regions. Many of these bottles have since disappeared from the market for various reasons. Whilst the bottles were initially promoted for their biodegradability it soon became clear that this could not last for ever as a selling point. On the one hand the biodegradation of the thick neck area of the bottle took too long, and on the other hand bottles are much too bulky and awkwardly shaped for industrial composting. First of all

5 Fig. 5.6: PLA bottles

they had to be shredded into flakes. Nevertheless some bottles have ridden the storm in situations where much closer attention was being paid to the origin of the plastic, namely from renewable resources. These bottles are either reclaimed by recycling, or they are burned as part of an energy recovery programme [73].

No wonder that it was the packaging industry that quickly recognised the huge potential for bioplastics. Users, packers, and brand owners are taking advantage of their userfriendly credentials. Disposal of used packaging made from bioplastic can be carried out in various ways (cf chapter 6). The preferred option today is energy recovery in waste incineration installations.

Bioplastics which are also biodegradable and compostable can also be reclaimed in composting or bio-gas installations [1].

5.2 CATERING As a rule catering products are short-lived, like packaging.

Once they have been used cups, plates and cutlery are thrown into the rubbish bin with any waste food clinging to them, and during festivals and other large scale events soon build up into considerable amounts. Here biobased plastics offer not only real ecological alternatives. They are also compostable and so can be

Fig. 5.7: PLA coated paper cups (picture: Huhtamaki Forks made from starch based plastic (picture: Novamont)

58 | 5 APPLICATIONSS

disposed of together with the food remnants.

Manufacturers have recognised this and now pots, cutlery, cups, dishes drinking straws or film wrapping for hamburgers – the whole range of catering accessories – are available made from bioplastics.

In addition to the extensive advantages already mentioned for bioplastics, their biodegradability also plays a special and important role in gardening and agriculture. By using them sensibly the gardener or farmer could save himself a great deal of work. Mulch film made from biodegradable plastic can be ploughed in after use and does not have to be laboriously picked up and disposed of as contaminated plastic waste at a rather high cost. Plant pots and seed trays break down in the soil and are no longer seen as waste.

Plant trays for flowers and vegetable plants, made from the right plastic, can be composted in the domestic compost heap together with kitchen and garden waste [1] Bioplastic twine, ties and clips (Fig. 5.9) are also cost savers and can be used for tying up tall plants such as tomatoes. Whilst materials currently used have to be picked up by hand after the harvest, or disposed of together with the green waste at higher cost, bioplastic alternatives can be disposed of on the normal compost together with plant waste [1].

5

5.3 HORTICULTURE AND AGRICULTURE

Fig. 5.7: Catering tableware (picture Permapack)

Fig. 5.8: Mulch film (picture: FKuR)

5.3 HORTICULTURE AND AGRICULTURE | 59

5 Fig. 5.9: Plant ties or clips can be disposed of together with green waste (picture: Novamont)

Fig. 5.11: A golf ball that degrades in water and that has a central core filled with fish food [74]

Fig. 5.10: Geotextiles reduce soil erosion or weed growth 60 | 5 APPLICATIONSS

Bioplastic, compostable, pre-sown seed strips and encapsulation for active substances are commonly used. Degradable film and nets are used in mushroom growing as well as for wrapping the roots of trees and shrubs ready for sale in garden centres. Film, woven fabric (Fig. 5.10) and nets made from bioplastics are used to hold back recently laid roadside banks and similar, and prevent soil erosion until they are stabilised by plants. Products used in cemeteries such as plant containers, pots or “everlasting� candles with biodegradable housings and other grave decorations can be composted after use right on the site. For those who operate and run golf courses biodegradable driving tees are an interesting alternative – they do not need to be collected up and the problem solves itself as they decompose [1]. Recently even a golf ball has been demonstrated that, if it accidentally lands in a pond or a lake, slowly breaks down and releases a cache of fish food (Fig. 5.11) [74].

In the field of medicine special bioplastics have been used for many years. Such bioplastics, that are resorbable, can be applied for several tasks [1]: thermoplastic starch, for instance, is an alternative to gelatine as a material for pills and capsules. PLA and its copolymers are used as surgical thread, as a carrier for implanted active substances, or to produce resorbable implants such as screws, pins, or plates that are degraded by the metabolism and so make a second surgery for their removal unnecessary.

Special characteristics of certain bioplastics make them a predestined material for hygiene items.

These materials allow water vapour to pass through them but remain waterproof and are already widely used as “breathing” biofilm for nappy liners, bed underlays, incontinence products, female hygiene products and disposable gloves [1].

In the huge personal care market more and more bioplastics are finding a use. Lipstick cases and jars for powders or creams are just as readily available, as were the first shampoo bottles made from biobased polyethylene. This is only a small selection of the huge number of packaging products already on the market.

Fig. 5.12: Biodegradable nappy lining (picture: [1])

Fig. 5.14: Shampoo and conditioner bottles made from bio-PE (picture: Procter & Gamble)

Fig. 5.13: CARGO PlantLove™ Cosmetics collection from Ingeo (PLA) (photo CARGO)

5.4 MEDICINE AND PERSONAL CARE | 61

5

5.4 MEDICINE AND PERSONAL CARE

Fig. 5.17: Computer keyboard with a cellulose plastic based lower housing and a hand-rest (black) made from lignin based plastic (picture: FKuR / Fujitsu)

5

5.5 CONSUMER ELECTRONICS Fig. 5.18: Computer mouse made from cellulose acetate (picture: Philipp Thielen)

Fig. 5.15: Sony Walkman with PLA (picture: Sony)

Fig. 5.16: Mobile telephone with a housing made from PLA/ kenaf (picture: NEC / Unitika)

62 | 5 APPLICATIONSS

In contrast to the medical area, or gardening, applications in the field of consumer electronics, biodegradability is not really an important issue.

Here, as with all durable goods, it is the biological origin of the materials used that is the important aspect. The first electronic equipment of this type and where biobased plastic was used included the Sony Walkman™. PLA was used here as early as 2002.

A very early mobile phone with a housing made from PLA and reinforced with kenaf fibres was launched in 2005. Today there are already a huge number of electronic devices on the market, from the computer mouse, through keyboards to headphone parts, all with a housing or components made from biobased plastic.

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As mentioned in chapter 3.1 Henry Ford in the USA had already started to experiment at the beginning of the last century with bioplastics based on wheat and soya for applications in automobile manufacture.

A starter housing made from an asbestos fibre reinforced synthetic resin, produced from wheat gluten, was among the first series applications for the 1915 Model T. Later Ford used an increasing number of parts made from bioplastics, such as glovebox lids, gear knobs, horn buttons, accelerator pedals, distributor covers, internal decoration, steering wheels, fascia panels, and later for a prototype trunk lid. Finally Ford gave the “green light” for the production of a totally plastic car. The bodywork was made exclusively of plastic, mostly from renewable resources. It consisted of 14 plastic panels fixed to a tubular framework. The panels and the frame each weighed about 113 kilograms. The total weight of the car was about 1043 kilograms – about two thirds of the weight of a steel car of around the same size [19].

Today Ford are testing the use of up to 40% soya based polyol for polyurethane components, firstly for seats, head rests or arm rests. In an initial project with a 2008 Ford Mustang the soya based content of the polyurethane parts was only 5% by weight [37]. Another pioneer in this process is Toyota. In the “Prius”, which is currently one of the most environmentally conscious cars in the world, the spare wheel cover is made from PLA with kenaf reinforcement. At the end of 2011 it was reported that Toyota was to launch a car where the internal surface covering was made from about 80 % bioplastic. The “Sai” hybrid limousine sold in Japan has amongst other things seat covers and carpets made from partly biobased PET [76].

Further examples are PLA based om/en/books/bioplastics.php “biotech materials”, that have been developed and used by Mazda [77].

These materials are not only interior injection moulded parts but are also used for seat covers. A partially biobased polyester material is used for seat covers by Honda. The polypropylene terephthalate (PPT) is made using a bio-PDO and a terephthalic acid which is petroleum based. In combination with petroleum based PET

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5.6 AUTOMOBILE MANUFACTURE

Fig. 5.19: Gear shift cover of a Mazda Premacy Hydrogen RE Hybrid made from biotech materials (picture: Mazda)

5.6 AUTOMOBILE MANUFACTURE | 63

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Fig. 5.20: Accelerator pedal made from PA 6.10 (picture: Philipp Thielen)

Fig. 5.21: Fuel connectors made from PA11 (picture: Arkema) Fig.5.22: Prototype application of a partially biobased elastomer (picture: DuPont)

64 | 5 APPLICATIONSS

fibres a “bio-fabric� is produced with a 30% to 40% content obtained from renewable resources [78].

The use of (partially) biobased polyamides has been developed and tested as part of a project by a Baden-WĂźrttemberg (Germany) cluster. In addition to a venting nozzle and fan housing an accelerator pedal made from PA 6.10 was also produced as prototypes [79].

There have also been a number of different developments in the field car tyres.

One of the big tyre manufacturers uses a filler made principally from a maize based bioplastics in his rubber mixture. In addition to the advantages of using a renewable resource this is also said to offer good grip and reduced rolling resistance, and claimed to result in about a 5% saving in fuel consumption. The tyre manufacturer is also working on the possible use of biobased isoprene as a component of the rubber [80, 81].

From Finland there is a tyre in which a softener is used based on rapeseed oil and replaces the petroleum based material.

In the engine compartment plastics based on renewable resources are also used. But this too is not new. Polyamide 11 made from castor oil has been used in automotive applications for more than 30 years and is eminently suitable for fuel lines and connectors, especially for the very aggressive bio-ethanol (E10 etc.) and biodiesel fuels.

A partially biobased elastomer was announced in the autumn of 2010 for a prototype airbag. This application, which is not yet in series production, does however show that there is a high level of interest right across the automobile industry and that there is a large number of possible uses.

5.7 TEXTILES

5

In the minds of many readers the word “polyester” is automatically linked to textiles and only at closer inspection is it seen as a “plastic”. It is therefore no wonder that most bio-polyesters are used to spin fibres and produce textiles. These are mainly PLA and PTT, but also other materials like PPT (see above regarding car seat covers).

The examples of the various applications are almost endless, and go from children’s shoes, to men’s business shirts and haute couture apparel. In fact textiles made from renewable resources are almost as old as the human race (linen, cotton etc.). Modern textiles made from renewable resources now however combine their “biological” origin with the technical properties of modern microfibre textiles such as, in particular, good moisture transmission so that sweating is (almost) no longer a problem.

Fig. 5.23: Swim fashion made from PTT fibres (picture: DuPont) Fig. 5.24: Baby shoes, PLA/PET blended fabric, soles: PLA compound [36] Fig. 5.25: BioSposa Gattinoni Haute Couture 100% Ingeo (PLA) (picture: Gattinoni) Fig. 5.26: Men’s shirt, mixed fabric with PLA fibres (picture: Olymp) Fig. 5.27: Versace Sport Fall/Winter collection in Ingeo (PLA) fiber with Ingeo (PLA) fiberfill (photo Versace Sport) Fig. 5.28: Rugs made from PLA fibres (picture: NatureWorks)

5.7 TEXTILES | 65

5.8 OTHER

5

“From the cradle to the grave” (or maybe we should say from “the nappy to the urn”) we have already mentioned a large number of “other” applications and yet the potential use of bioplastics is virtually unlimited. In this section we will be showing just a few of the other examples. The desktop accessories are made from a PLA of Chinese origin and produced in Hungary. In 2010 they were among the five finalists for the Bioplastics Award. Adhesive tape made from cellulose materials or biaxially oriented PLA (BoPLA) have now also been combined with biobased adhesives. In the sport and leisure sector the number of applications is steadily growing. The handle on a Nordic walking pole made of partially biobased polyamide 6.10 was launched in 2009, as were ski boots with certain components made from biobased elastomers. The sports range was also complemented by amongst other things spectacles and sun glasses with high quality optical lenses made from clear bio-polyamide. Children’s sand box toys are on the market made from PHA or cotton cellulose, and model railways are enhanced by the addition of small, highly detailed buildings made from PLA. The list could go on and on...

Fig. 5.31: Handle of a Nordic walking pole made from bio-PA 6.10 (picture: DuPont)

66 | 5 APPLICATIONSS

Fig. 5.30: Adhesive tape made from BoPLA (picture: Taghleef Industries)

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Fig. 5.29: Desktop articles made from PLA

Fig. 5.32: Ski boot with the upper cuff made from partially biobased elastomer (picture: DuPont)

Fig. 5.33: Play sand box made from cotton cellulose and other starch based bioplastics (picture: BioFactur)

Fig. 5.34: Farmhouse for model railways made from PLA (picture: Vollmer) 5.8 OTHER | 67

6

END OF LIFE / DISPOSAL / CLOSED LOOPS

6

And what happens when these lovely plastic products eventually get broken, worn out, or are simply not required any longer?

Here we have a whole range of so-called “End of Life” scenarios, which can be used, depending on the material, the application and its condition. These are basically: 1 Recycling 1.1 Material recycling 1.2 Chemical recycling 1.3 Energetic recycling or thermal recycling (cf. 3) 2 Composting 3 Energy recovery 4 Rubbish tips/land fill

6.1 RECYCLING The word “recycling” covers a wide range of general processes in which products that are no longer needed (mainly trash) are converted into a secondary material [2].

In the case of plastic recycling, collection and sorting are to some extent an important prerequisite for the recycling procedures presented here.

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Material recycling, physically or mechanically, is, in simple http://bioplasticsmagazine.com/e terms, the shredding, cleaning and remelting, and regranulating of plastic waste. In this process the chemical make-up of the material remains unchanged and the secondary raw material can generally be re-used without any losses. Such recyclate, in granulate form can be used for a wide range of new plastic products, depending on its purity and quality. Extremely pure waste such as production waste (trimmed edges of film, runners, etc.) are often fed straight back into the same production process. However, very mixed, unsorted and dissimilar plastic waste can, under heat and pressure, often be recycled to make products with undemanding tolerances such as park benches or 68 | 6 END OF LIFE / DISPOSAL / CLOSED LOOPSS

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embankment supports. Most cases of recycling lie somewhere in between these extremes. If, in a new application, a recycled plastic product is inferior in quality to the products initially produced we talk about “downcycling”. This is something that one tries hard to avoid or to minimise as much as possible. In ideal cases plastic is used several times in what is known as “cascade recycling”, for instance in a detergent bottle, a shopping bag then a rubbish sack and finally a park bench. At the end of a cascade recycling loop there is also the possibility of making use of the material for thermal recycling (see 6.3). Most bioplastics can be made ready for use in material recycling. In some cases, depending on the circumstances, additional steps are required. It may, for example, be necessary for PLA to go through an additional step of polycondensation, or a special crystallisation stage [83].

In order to be able to recycle any specific plastic economically a “critical amount” is nevertheless needed. ´ 6.1.2 CHEMICAL RECYCLING The old plastic material can not only be remelted and regranulated for a new application but in some cases it may also be broken back down into its chemical building blocks (monomers). This is known as chemical recycling or feedstock recovery. A particularly interesting example here is found in the field of bioplastics – namely the chemical recycling of PLA. In installations such as are currently operating in Belgium or California the polylactic acid is reconverted into lactic acid and so can then be converted into new PLA or be used for other purposes [84].

w Sample the book at 6.2 COMPOSTING

om/en/books/bioplastics.php Plastics that are biodegradable under certain conditions and are completely broken down by micro-organisms into CO2, water and biomass can be composted. Attention should be paid here to the relevant standards such as EN 13432, EN 14855, ASTM D6400 and similar (cf. chapter. 9) There is still some controversy about the sense (or lack of sense) when it comes to composting biodegradable plastics.

Disposal by composting is one new, additional option for plastic products of that type, yet there are also people who say that composting alone brings no real additional benefit. It is no more than “cold incineration”.

6.2 COMPOSTING | 69

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Fig. 6.1: Industrial composting in Dortmund/Germany

There are however plenty of examples where biodegradability, or disposal by composting, do in fact bring additional benefits. Unsold or rotting fruit and vegetables in a supermarket can be collected up and disposed of together with compostable packaging. At large scale events catering cutlery, tableware and food remnants can be taken together to a composting facility. As early as 2005, on the Catholic World Youth Day, there were about 7 million compostable catering units used.

When growing tomatoes in a greenhouse plastic clips have been used for many years to hold the tomato plants firmly against the support canes and allow them to grow upwards. After the tomato harvest these clips, made of compostable plastic, can be disposed of with the green plant residues. Despite a higher cost of acquisition compared to conventional plastic clips they do offer the grower financial benefits. As a final example we can once again mention mulch film which after the harvest can be ploughed into the ground (cf. chapter 5.3).

6.3 ENERGY RECOVERY OR THERMAL RECYCLING

Fig. 6.2: Mulch film (Picture: Novamont)

70 | 6 END OF LIFE / DISPOSAL / CLOSED LOOPSS

Renewable resources can in fact be used immediately to generate energy (wood pellets, bio-fuels, biogas etc.) but they can better first be used to produce something more useful – namely bioplastic parts. These can, after a long useful life, and after being recycled a maximum number of times, still be burned and the stored up energy finally used. “Bioplastics hold solar energy on loan”. In this respect there are plenty of people demanding that renewable resources are not used (immediately) for the purpose of generating energy [85, 86]. Wind, the sun, and water can all be used to generate renewable energy - but not to make plastics.

The generation of heat and other forms of energy (electricity) by incineration of plastic waste

is currently the most commonly used process in Europe for reclaiming the value of such waste, and as long as sufficient quantities are not available for economical material recycling it is, in the view of many experts, the most logical option. The high level of heat generated when incinerating plastics makes them an ideal substitute for coal or heating oil. Whether biobased or obtained from fossil sources there is no technical difference in the value recovery process. In the case of biobased plastics it is possible, however, to obtain renewable energy from the biogenic carbonates – and that is a powerful advantage [87].

Another option for using the energy available is biogasification, also called anaerobic digestion (AD). The possibility of using the waste from biodegradable plastics in biogas installations and to convert it into useful methane is being intensively investigated at the moment [88].

The worst solution for disposal of bioplastics (as for bio-waste of all kinds) is the rubbish dump or land fill. By dumping the materials on a waste disposal tip all kinds of plastics lose the opportunity for other useful applications.

Among the more unpleasant possibilities is the formation of methane from bio-waste and bioplastics in the lower layers where there is a shortage of oxygen. This methane, which if allowed to leak uncontrolled, is 23 times more effective than CO2 as a greenhouse gas. In Germany, since 2005, it has not been legal any more to dump rubbish without having it previously thermally or biologically treated (incineration or decomposition by rotting) [89].

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6.4 LAND FILL

Fig. 6.3: Land fill (picture: Ropable)

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6.5 CLOSED LOOPS “Closed loop systems and resource efficiency with bioplastics” is the name of a fact sheet from the European Bioplastics association. In there we can read, amongst other things: Biobased carbon sequestered in the material can be recycled in technical closed loops or by natural processes. This way bioplastics enable intelligent use of resources and ensure a high added value in a low carbon economy.

As with conventional plastics, the manner in which bioplastics waste is actually recovered depends on the type of product and bioplastics material used, the inherent quantities and the recovery systems available.

Bioplastics can represent a valuable component in the closed loop system and thereby make a considerable contribution to sustainable development. To achieve this, they require time and successful market introduction. The European Lead Mar¬kets Initiative for Biobased Products acknowledges bioplastics as a valuable building block of a future bio-economy. Legislators should promote bioplastics and enable all recovery and recycling options. The consumer, the environment and not insignificantly, the waste industry will benefit from these new opportunities.

[87].

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74 | 7 THE MARKETS

THE MARKET One can search in vain for official statistics on the development of the market for bioplastics. However certain companies offer their findings in commercial studies on the subject [90]. A source of market information is found in the publications and press releases of the indzstry association European Bioplastics in Berlin. Cellulose materials are not covered here as these have been in use for many years. Thermoset resins such as epoxy resins, unsaturated polyester resin or polyurethanes with a certain amount of renewable resource material are also not covered as are rubber or conventional thermoplastics that are filled using natural fibres or wood flour [90].

In a press release at Interpack 2011 European Bioplastics estimated that the global production capacity for bioplastics was expected to more than double between 2010 and 2015. For the end of 2011 it was forecast that the 1 million tonne barrier would be breached [91].

As can be seen from Fig. 7.1 the production capacity for bioplastics will increase from around 700,000 tonnes in 2010 to about 1.7 million tonnes by 2015. This is calculated to be equivalent to a commercial market value of about 7.5 billion Euros [92]. But the graphic chart also shows another trend when one combines total global production volume. In 2004 the bioplastics industry, at 400,000 tonnes, still produced predominantly biodegradable material (as opposed to 300,000 tonnes biobased but not biodegradable plastics). This ratio, despite an overall growth, is being reversed. According to a market study by Professor Endres of the IfBB (Institute for Bioplastics and Biocomposites), at University of Applied Sciences and Arts Hanover, Germany, biobased but durable plastics by 2015, at around 1 million tonnes, will represent the majority of the production capacity. Biodegradable materials do however exhibit a clear growth pattern and by then will reach about 700,000 tonnes.

One reason for the above situation is the increasing availability of so-called “drop in bioplastics�. These are biobased (and partially biobased) standard plastics such as polyethylene, polyamide or PET. They are produced from the start in large scale installations and in suitably large quantities. Because, in com-

parison with petroleum based plastics, these plastics do not offer any improvement in their performance characteristics they are right from the start in direct price competition with their conventional counterparts which means that the bigger plants play a greater role [90].

Fig. 7.2 shows the production capacities for bioplastics broken down by type of plastic for the year 2010 and the forecast until 2015. It can clearly be seen here that the higher anticipated capacities will have a major influence on drop-in solutions such as bio-PE and bio-PET.

Fig. 7.1: Global production capacities for bioplastics (Source: European Bioplastics / IfBB, Hanover)

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1.710

1.500

1.000 metric tons

714

1.000

724

500

996

428 318 180 6

0

174 2008

23

295

296

2009

2010

Biodegrable (incl. not biobased)

2015

Durable (biobased)

Total Capacity

Prognosis 7 THE MARKET | 75

in metric tons

Bio-PE

200.000

28 %

Biodegrable Starch Blends

117.800

16 %

PLA

112.500

15 %

PHA

88.100

12 %

Biodegradable Polyesters

56.500

8%

Bio-PET

50.000

7%

Regenerated Cellulose2

36.000

5%

Bio-PA

35.000

5%

Cellulose Derivatives1

8.000

1%

PLA-Blends

8.000

1%

Durable Starch-Blends

5.100

1%

Others

7.500

1%

724.500

100 %

Total 1

only cellulose | 2 only cellulose foils

Fig. 7.2: Production capacities for bioplastics broken down by type of plastic (left 2010, right 2015 forecast) (Source: European Bioplastics / IfBB, Hanover)

7

Despite the enormous growth figures described above bioplastics are still only at the beginning of their development. In a total market for plastics of around 250 million tonnes (2010 [90]) and an estimated market of 330 million tonnes in 2015 [93] bioplastic accounts for a mere 0.027% (2010) to 0.5% (2015). From a purely technical point of view however up to 90% of all plastic could be switched from fossil resources to renewable resources.

In the short and medium term however this switchover would not be possible in terms of the economic obstacles to overcome and the limited short term availability of suitable biomass [94].

Cost development An important question is about the prices and the price development of bioplastics.

Today bioplastics are in most cases two to four times more expensive than the major conventional plastics such as polyethylene or PET. This however, is expected to to diminish as the oil price rises further and bioplastics manufacturing plants become larger and benefit from „economies of scale“.

When the local biological feedstock is particularly cheap, as it is in Brazil, large bio-polyethylene plants may already be close

76 | 7 THE MARKETS

in metric tons

Bio-PE

450.000

26 %

Bio-PET

290.000

17 %

PLA

216.000

13 %

PHA

147.100

9%

Biodegradable Polyesters

143.500

8%

Biodegradable Starch Blends

124.800

7%

Bio-PVC

120.000

7%

Bio-PA

75.000

5%

Regenerated Cellulose1

36.000

2%

PLA-Blends

35.000

2%

Bio-PP

30.000

2%

Bio-PC

20.000

1%

Others

22.300

1%

1.709.700

100 %

Total 1

only hydrated cellulose foils

7

to being cost-competitive with oil-based alternatives. But more generally, the crude oil for a kilo of plastic costs around â‚Ź 0.20 but the corn, a key source of feedstocks for bioplastics currently (August 2011) costs about twice this amount [107].

On the other hand it should not only be looked at the raw material cost. For certain applications the end-of-life can also contribute positivel to the total system cost. For example the mulch film or the tomato clips mentioned above offer significant cost advantages in the disposal stage. Thus the total system cost can be lower, even when the raw material is more expensive.

7 THE MARKET | 77

8

POTENTIAL AND PERSPECTIVES 8.1 FURTHER DEVELOPMENTS As discussed in the previous chapter, the market is expected to enjoy double-figure growth in the coming years. The percentage of bioplastic production represented by the various regions of the world is shown in Fig. 8.1.

During 2010 South America, North America and Europe, followed by Asia were the leading regions. According to Endres [92] it is expected that in the next few years in particular South America and Asia, as well as North America, will install additional capacity. Hence future growth will not be in Europe, even though the first bioplastics were largely developed in Europe. For 2015 European bioplastic production capacity is forecast to be around 0.5 million tonnes, which is less than 1% of Europe’s total plastics production [92].

8

Preview S Fig. 8.1: Production capacities for bioplastics broken down by region (2010) (Source: European Bioplastics / IfBB, Hanover)

you can order th

Australia 0,5

http://bioplasticsmagazine.com/e South America 27,6

Europe 26,7

in % total: 725.000 t

North America 26,7

78 | 8 POTENTIAL AND PERSPECTIVES

Asia 18,5

One is constantly hearing the question concerning the availability of agricultural land, and discussed in relation to world hunger. Because this is a very sensitive topic we have simply gathered here a few facts and figures.

An important point in this respect (according to Endres [92]), is that on the one side there is the argument about the long term availability of agricultural land for the sustainable production of raw materials for plastics, and on the other side there is the problem that the currently available fossil resources are being used much more rapidly than they can regenerate.

With plastics accounting for between 4% and 7% of total petroleum consumption, biobased plastics are not in a position to rescue the world from a shortage of oil. The plastics industry can however, by using biobased plastics, to a certain degree make itself more independent from the increasing, and at the same time fluctuating, price of oil if there is enough agricultural land for this purpose. Furthermore biobased plastics offer the prospect that those important materials known as plastics will continue to be available for the widest range of applications.

Depending on the type of bioplastic, the type of plants used, or the relevant agricultural raw material the average yield is from 2 to 4 tonnes of bioplastic per hectare [95, 97]. According to the estimates in chapter 6.3 it can be assumed that for 2015 the forecast world production capacity for bioplastics will require around 500,000 hectares of agricultural land. This represents about 0.03% of the agricultural land used worldwide, i.e. around 1.5 billion hectares. Even if the whole world plastics production capacity were to switch to biobased plastics only 4 % to 5% of the agricultural land available world-wide would be required [86, 92]. om/en/books/bioplastics.php In total there are on the earth about 3.3 billion hectares of land which could potentially be used for agricultural purposes, and with natural irrigation. This land is used for agriculture (1.5 billion hectares, see above), dwellings, streets, road and rail routes (100 million hectares), protected areas (330 million hectares) and forestry (800 million hectares). This leaves about 570 million hectares in the various geographical regions that could be used for production. In the European Union alone there are about 8 million hectares that could be used for the production of bioplastics or the generation of bio-energy. The majority of this land is to be found in the new EU member states in Eastern Europe [95, 96].

w Sample the book at

8.2 DO WE IN FACT HAVE ENOUGH AGRICULTURAL LAND? | 79

8

8.2 DO WE IN FACT HAVE ENOUGH AGRICULTURAL LAND?

8

Furthermore, the quantity of land required for bioplastics would become available simply as a result of the constantly increasing yield per hectare thanks to the advances being made in agricultural techniques. In recent decades agricultural producers have increased their yield on average by one or two percent per annum. This is a result of scientific advances, optimising the production processes, the use of machinery, effective fertilisers, methods of plant protection and the use of new or improved plant strains [95].

If, in addition, the amount of unused, waste biomass is reduced (in the Western World, for instance, about 45% of food production is still thrown away) there would still be enough agricultural land available to feed the world population and for the production of bioplastics.

For biofuels or energy recovery of biomass in general there are different quantities and land requirements. We therefore once again point out here that, as made clear in chapter 7, a “material use” is preferred (at least temporarily) over “energetic use” of biomass or renewable resources respectively [85, 86].

After all, the wind, the sun and water power are also renewable sources of energy – not for making plastics however.

80 | 8 POTENTIAL AND PERSPECTIVES

8 8.2 DO WE IN FACT HAVE ENOUGH AGRICULTURAL LAND? | 81

9

LEGAL AND REGULATORY BACKGROUND Most of the comments and data in this section refer to the situation in Germany. They are expanded by those regulations that also apply in the EU and the USA. The German recycling and waste directives require the manufacture of products which are so designed that during their production and use the amount of waste is minimised. Certain general assumptions include the fact that no noxious by-products or additives must find their way into the natural waste disposal cycle. National and international standards regarding the degradability of polymer materials and products have meanwhile been established to cope with these problems. [1].

Fig 9.1: The “seedling“ (European Bioplastics)

9.1 STANDARDS AND CERTIFICATION REGARDING “COMPOSTABILITY”

These standards refer to the compostability of packaging - (EN 13432 [98] or more generally to plastics (EN 14995 [99], ASTM D6400 [100]).

The compostability of a plastic by confirmed biological degradation and as part of an industrial composting installation is defined (cf. chapter 6.2). The time-related conversion of carbon into CO2, the loss of physical properties (weight, size) as well as the toxicological properties of the compost produced, are measured in a laboratory [101].

If bioplastics, and the products made from them, meet the requirements of these standards they can be registered and have http://bioplasticsmagazine.com/e the right to display an appropriate registered logo [1]. In Europe DIN CERTCO (Germany) and Vinçotte (Belgium) belong to independent certification associations. In the USA this is governed by the BPI (Biodegradable Products Institute). They establish a certificate of conformity for the materials (i.e. an assessment of the material’s conformity with the standard) and confirm the manufacturer’s right to display a suitable badge or label for compostable products. A material that has the right to carry

9

Preview S

Fig. 9.2: The OK-CompostLogo (Vinçotte)

Fig. 9.3: The US Compostable Logo (BPI, US Composting Council)

82 | 9 LEGAL AND REGULATORY BACKGROUNDS

you can order th

such a compostability label will completely degrade in the composting installation within 6 to 12 months. Figures 9.1 to 9.3 show the most well-known logos [102, 103, 104].

The compostability standard laid down in EN 13432 is backed up by other related requirements. These include the EU Packaging Directive 94/62/EG and a draft for an EU Biowaste Directive. In Germany there is a packaging ordinance (with regulations concerning compostable packaging) and a bio-waste ordinance (with regulations for biodegradable products made from renewable resources) [1].

9.2 THE PACKAGING ORDINANCE The German packaging ordinance (VVO), amended in 2005, regulates the way in which used packaging must be treated.

For certified compostable plastic packaging made from bioplastics a special regulation was added to the effect that this type of packaging is exempted, until December 31st 2012, from the requirements described in § 6 of VVO and the DSD charge (the “Green Dot” waste disposal system charge). The producer and the marketer must, however, ensure that as much of the packaging as possible is being reclaimed and recovered [1].

w Sample

As has been mentioned several times above, the biological origin (renewable resources) of plastics is taking on a greater importance than their compostability. Hence the efforts to have confirmation and quantification of the material’s “biobased credentials” have also increased. The two basic differences in the way a biobased content can be defined have om/en/books/bioplastics.php already been discussed in chapter 3.2. The certifications in question are based on the carbon content, which can be accurately measured using the radiocarbon method. The American standard ASTM D6866 gives guidance on how the carbon content (12C vs. 14C) should be determined [105].

the book at

9.3 STANDARDS AND CERTIFICATION REGARDING “BIOBASED” | 83

9

9.3 STANDARDS AND CERTIFICATION REGARDING “BIOBASED”

Fig. 9.4: OK-biobased Logo indicating biobased carbon content

between 20 and 40 % biobased

SED 20 - 50 BA %

IO

SED 50 - 85 BA %

Fig. 9.5: DIN-Geprüft Biobased (DIN CERTCO)

84 | 9 LEGAL AND REGULATORY BACKGROUNDS

B

IO

between 60 and 80 % biobased

more than 80 % biobased

Vinçotte in Belgium were the first to offer certification and the use of their “OK Biobased” logo. One to four stars are awarded and displayed on the logo depending on the material’s “biobased” carbon content (Fig. 9.4).

DIN CERTCO now also offers such certification where the biobased content is given in groups of percentages too (Fig. 9.5).

In the USA there has been a programme running for a few years and known as “BioPreferred®”. This programme obliges public bodies to purchase products that have the maximum possible content of material from renewable resources. A certification system has evolved from the programme which is based on percentage values determined in accordance with ASTM D6866 and which awards the “USDA CERTIFIED BIOBASED PRODUCT” logo (Fig. 9.6) stating the percentage of renewable resources.

B

B

9

Fig. 9.6: USDA certified biobased product (USDA)

between 40 and 60 % biobased

B IO

D > 85 ASE %

9 9.3 STANDARDS AND CERTIFICATION REGARDING “BIOBASED” | 85

10

SUGGESTED FURTHER READING

FREQUENTLY ASKED QUESTIONS... ... on the use of agricultural resources for the production of bioplastics, European Bioplastics FAQ Agriculture at at http://en.european-bioplastics.org/multimedia/

FACT SHEETS (at http://en.european-bioplastics.org/multimedia/) on the subjecs of •

Industrial composting (in English)

•

Home composting (in English))

•

Mechanical recycling (in English)

•

Chemical recycling (in English)

•

Energetic Recycling (in English)

•

Anaerobic digestion (in English)

•

Land fill (in English)

10

FACT SHEETS – SHORT VERSIONS (at http://en.european-bioplastics.org/multimedia/) on the subjects of •

Bioplastics (German and English)

•

End of Life (German and English)

•

Packaging (German and English)

•

Shopping bags (German and English)

•

Green chemistry (German and English)

•

Renewable resources (German and English)

86 | 10 GESTED FURTHER READING

BOOKS A number of books are mentioned in the literature list (chapter 12). Particularly recommended are: •

Endres, H.-J., Siebert-Raths, A.: Engineering Biopolymers, Carl Hanser Verlag, 2011

•

Stevens, G.: Green Plastics: An Introduction to the New Science of Biodegradable Plastics; Princeton University Press, 2001

10

INTERNET And of course the Internet (see chaper 11 on the following page)

10 SUGGESTED FURTHER READING | 87

11

SOURCES OF INFORMATION ON THE INTERNET www.bioplasticsmagazine.com

Trade magazine

www.european-bioplastics.org

Industry association

www.fnr.de

Agency for renewable resources

www.bio-based.eu

News portal (subscription required)

www.bio-plastics.org

News portal

http://bioplastic-innovation.com News portal and blog

Preview Sample www. bpiworld.org

Compostability certification

www.dincertco.de

Compostability certification

www.okcompost.be

Compostability certification (Vinçotte)

programme for youwww.biopreferred.gov can order theUSDA book at purchasing by public bodies

http://bioplasticsmagazine.com/en/books/bioplastics.php www.greenplastics.com A “Wiki” on bioplastics by Prof. Stevens, Princeton A collection of further useful links

www.biowerkstoffe.info

Agency for renewable resources

11

www.biopolymer.net

88 | 11 SOURCES OF INFORMATION ON THE INTERNET

11 11 SOURCES OF INFORMATION ON THE INTERNET | 89

12

LIST OF REFERENCES [1]

Lörcks, J.: Biokunststoffe, Broschüre der FNR, 2005

[2]

N.N., Wikipedia, Internet access during June-Dec. 2011

[3]

N.N.: Plastics – the Facts 2010, An analysis of European plastics production, demand and recovery for 2009,.

Plastics Europe, Brüssel, 2010

[4]

Endres, H.-J., Siebert-Raths, A.: Engineering Bioplymers, Carl Hanser Verlag, 2011

[5]

N.N.: DIN EN ISO 14855-1

[6]

de Wilde, B.: Anaerobic Digestion, bioplastics MAGAZINE, Vol 4., Issue 06/2009

[7]

Thielen, M.: Industrial Composting, bioplastics MAGAZINE, Vol 4., Issue 02/2009

[8]

Thielen, M.: Home Composting, bioplastics MAGAZINE, Vol 3., Issue 06/2008

[9]

N.N.: Leistungsfähig und bioabbaubar, Pressrelease P-09-445, BASF 2009

[10] N.N.: bioplastics MAGAZINE, Vol. 6, Issue 03/2011, S. 6 [11] N.N.: Position Paper „ Oxo-biologisch abbaubare Kunststoffe“ European Bioplastics, Berlin, 2009 [12] N.N.: Sustainable Plastics, FKuR statement to Oxo degradable plastics, FKuR Kunststoff GmbH, Willich, 2009 [13] N.N.: www.tecnaro.de, Internet access, July 2011 [14] N.N., www.duponttateandlyle.com, Internet access June/July 2011 [15] N.N., www.genomatica.com, Internet access June/July 2011 [16] Bonten, C.: Historie und Moderne von Biokunststoffen, Vortrag Thementag „Biokunststoff im Automobil“, BioPro Baden Württemberg, 10.6.2011 [17] Worden, E.C.: Nitrocellulose industry. New York, Van Nostrand, 1911, S. 568. (Parkes, English Patent 2359 from the year 1855) [18] Bonten, C.: Generation Zero - Non-food stocks bioplastics were the very beginning! bioplastics MAGAZINE, Vol 3, Issue 05/2008 [19] N.N.: http://www.chanvre-info.ch/info/de/Zu-Henry-Fords-Auto. html, Internet access Jun4 2011

12

[20] Carus, M.; Scholz, L.: How to Measure the Biobased Content, bioplastics MAGAZINE, Vol. 5, Issue 03/2010 [21] Bastioli, C.: Basics of Starch-Based Materials, bioplastics MAGAZINE, Vol. 4, Issue 05/2009 [22] Kaeb, H. personal information 2011

90 | 12 LIST OF REFERENCES

[23] Zepnik, S.; Kesselring, A; Kopitzky,R.; Michels, C.: Basics of Cellulosics, bioplastics MAGAZINE, Vol. 5, Issue 01/2010 [24] Buddrus, J.: Grundlagen der Organischen Chemie, Walter de Gruyter Verlag, Berlin, 4th edition, 2011, S. 897 [25] Gaumann, U.; Werner T.: A Bio-Cover for the Airbag, bioplastics MAGAZINE, Vol. 6, Issue 01/2011 [26] N.N.: www.pebax.com, Internet access, July 2011 [27] N.N.: Aufschwung für Biowerkstoffe: Zweistelliges Wachstum trotz Krise, Pressrelease of nova-Institut 23.11.2009 [28] Fink, H.-P.: Basics of Lignin, MAGAZINE, Vol. 6, Issue 01/2011 [29] Seydibeyoğlu, M. Ö. et.al: New Biobased Polyurethane from Lignin and Soy Polyols, MAGAZINE, Vol. 5, Issue 05/2010 [30] Britton, R.: Update on Mouldable Particle Foam Technology, iSmithers, 2009 [31] N.N.: PHA from Switchgrass – a Non-Food-Source Alternative, bioplastics MAGAZINE, Vol. 3, Issue 05/2008 [32] N.N.: Improved PHA Production in Tobacco, bioplastics MAGAZINE, Vol. 6, Issue 02/2011 [33] Fernyhough, A.: From Waste 2 Gold: Making bioplastic products from biomass waste streams, bioplastics MAGAZINE, Vol. 2, Issue 04/2007 [34] de Vos, S.: Improving heat-resistance of PLA using poly(D-lactide), bioplastics MAGAZINE, Vol. 3, Issue 02/2008 [35] N.N.: Mazda introduced ‘Biotechmaterial’ for interior applications, bioplastics MAGAZINE, Vol. 3, Issue 02/2008 [36] Inomata, I.: The Current Status of Bioplastics Development in Japan, bioplastics MAGAZINE, Vol. 4, Issue 01/2009 [37] N.N.: The Coca-Cola PlantBottle, bioplastics MAGAZINE, Vol. 5, Issue 06/2010 [38] N.N.: Bio-PET, bioplastics MAGAZINE, Vol. 5, Issue 06/2010 [39] Morgan, K.: Completing the Puzzle: 100% plant-derived PET, bioplastics MAGAZINE, Vol. 6, Issue 04/2011 [40] N.N.: Carbohydrate Route to Paraxylene and Terephthalic Acid, US Patent 2010/0331568, 30. 12. 2010

12

[41] N.N.: Sorona® EP for new Toyota compact van, bioplastics MAGAZINE, Vol. 6, Issue 04/2011 [42] N.N.: http://www2.dupont.com/Renewably_Sourced_Materials, Internet access July 2011

12 LIST OF REFERENCES | 91

[43] Domininghaus, H.: Die Kunststoffe und ihre Eigenschaften, VDI Verlag, Düsseldorf [44] Baur, E.; Brinkmann, T;. Osswald, T.; Schmachtenberg, E.: Saechtling Kunststoff Taschenbuch, Carl Hanser Verlag, München Wien [45] Stoeckhert: Kunststoff Lexikon, Carl Hanser Verlag, Müchnen Wien [46] Becker, Bottenbruch, Binsack: Technische Thermoplaste.

4. Polyamide, Carl Hanser Verlag, Müchnen Wien [47] Thielen, M.: Basics of bio-polyamides, bioplastics MAGAZINE, Vol. 5, Issue 03/2010 [48] N.N.: K-show-review, bioplastics MAGAZINE, Vol. 2, Issue 04/2007, Seite 8 [49] N.N.: Acrylglas aus Zucker, Pressrelease of UFZ (2008), www.ufz.de/index.php?de=17387, Internet access July 2011 [50] Grimm, V. et.al.: Biomasse – Rohstoff der Zukunft für die chemische Industrie, Herausgeber: Zukünftige Technologien Consulting der VDI Technologiezentrum GmbH, Düsseldorf, 2011 [51] Morschbacker, A et.al.: Basics of Bio-Polyolefins, bioplastics MAGAZINE, Vol. 5, Issue 05/2010 [52] N.N.: Green Propylene, Report abstract, Nexant, www.chemsystems.com, Internet access 2011 [53] Smith, C.: Braskem commits to producing biobased polypropylene, Plastics News online, 28.10.2010 [54] Mannermaa , T.: The First Step to Sustainable Composites, bioplastics MAGAZINE, Vol. 6, Issue 03/2011

Preview S

[55] N.N.: Full System Ahead: The Rise of Biobased Thermoset, bioplastics MAGAZINE, Vol. 6, Issue 03/2011 [56] N.N.: Solvay launches project to build an epichlorohydrin production plant in China, www.solvaychemicals.com, Internet access July 2011

you can order th

[57] Stemmelen, R. et.al: A Fully Biobased Epoxy Resin from Vegetable Oils, Journal of Polymer Science Part A: Polymer Chemistry, 49: 2434–2444. doi: 10.1002/pola.24674

http://bioplasticsmagazine.com/e

[58] N.N.: bioplastics MAGAZINE, Vol. 6, Issue 06/2010, S. 14 [59] Carus, M., Piotrowski, S.: Land Use for Bioplastics, Biowerkstoffreport, nova-Institut, Issue 06/2009 [60] N.N.: www.biopolymers.nl, Internet access July 2011

12

[61] Verlinden, R.; Hill, D.; Kenward, M.; Williams, C.; PiotrowskaSeget, Z; Radecka, I: Production of polyhydroxyalkanoates from waste frying oil by Cupriavidus necator, www.amb-express.com/content/1/1/11, Internet access, Dec. 2011

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[62] Román-Leshkov, Y; Barrett, C.J., Liu, Z.Y.; Dumesic, J.A.: Production of dimethylfuran for liquid fuels from biomass-derived carbohydrates, Nature 447, 982-985 (21 June 2007).

[63] Thielen, M..: Basics of Compounding Bioplastics, bioplastics MAGAZINE, Vol. 5, Issue 04/2010 [64] Kühnen, U.; persönliche Information, Coperion, Stuttgart, Juli 2010 [65] N.N.: How to Produce BOPLA Films, bioplastics MAGAZINE, Vol. 5, Issue 06/2010 [66] Thielen, M., Hartwig, K., Gust, P.; Blasformen von Kunststoffhohlkörpern, Carl Hanser Verlag, 2006 [67] N.N.: www.actimel.de/umweltfreundliche-verpackung.html, Internet access, August 2011 [68] Yoder, L.; Plastic Technologies, Inc.: Basics of Stretch Blow Moulding, bioplastics MAGAZINE, Vol. 6, Issue 04/2011 [69] Michaeli, W.: Einführung in die Kunststoffverarbeitung, Carl Hanser Verlag, München, Wien, 1999 [70] Oberbach, K.; Baur, E.; Brinkmann, S.; Schmachtenberg, E.;: Saechtling Kunststoffhandbuch, Carl Hanser Verlag, München, Wien, 2004 [71] N.N.: several articles in MAGAZINE, Vol. 5, Issue 01/2010 [72] Manjure, S:; PLA for Paper Coating, bioplastics MAGAZINE, Vol. 6, Issue 05/2011 [73] Thielen, M.: The Ritz-Carlton goes Prima, bioplastics MAGAZINE, Vol. 5, Issue 04/2010

w Sample

[74] Schnerr-Laube, B.: Golf Players Feed Fish, bioplastics MAGAZINE, Vol. 5, Issue 04/2010 [75] N.N.: Bioplastics in Automotive Applications, bioplastics MAGAZINE, Vol. 4, Issue 01/2009 [76] N.N.: Toyota setzt auf Biokunststoff, http://nachrichten.rp-online.de/auto/toyota-setzt-auf-biokunststoff-1.2509333 (Internet access Nov. 2011)

the book at

[77] N.N.: Mazda introduced ‘Biotechmaterial’ for interior applications,

bioplastics MAGAZINE, Vol. 3, Issue 02/2009 om/en/books/bioplastics.php

[78] N.N.: Bioplastics in Automotive Applications, bioplastics MAGAZINE, Vol. 2, Issue 01/2007 [79] N.N.: Bio-Polyamides for Automotive Applications, bioplastics MAGAZINE, Vol. 5, Issue 01/2010

12

[80] N.N.: Bio-Tyres save energy and CO2 , bioplastics MAGAZINE, Vol. 2, Issue 01/2007 [81] N.N.: Concept Tyres Made with BioIsoprene™, bioplastics MAGAZINE, Vol. 5, Issue 01/2010

12 LIST OF REFERENCES | 93

[82] N.N.: LANXESS produziert weltweit ersten EPDM-Kautschuk auf biologischer Basis, Pressrelease 2011-00182, Lanxess Deutschland GmbH, Leverkusen, 2011 [83] N.N.: persönliche Information, EREMA, 2011 [84] Willocq, J.: A new Cradle-to-Cradle Approach for PLA, bioplastics MAGAZINE, Vol. 4, Issue 05/2009 [85] Carus, M.; Carrez, D.; Kaeb. H.; Ravenstijn, J.; Ventus, J.: Level Playing Field for Biobased Chemistry and Materials, bioplastics MAGAZINE, Vol. 6, Issue 03/2011 [86] Carus, M.; Raschka, A.: Agricultural Resources for Bioplastics, bioplastics MAGAZINE, Vol. 6, Issue 06/2011 [87] N.N.: Fact Sheet: Kreislaufwirtschaft und Ressourceneffizienz mit Biokunststoffen, European Bioplastics e.V., 2011 [88] de Wilde, B.: Basics of Anaerobic Digestion, bioplastics MAGAZINE, Vol. 4, Issue 06/2009 [89] N.N.: AbfAblV – Abfallablagerungsverordnung (Verordnung über die umweltverträgliche Ablagerung von Siedlungsabfällen) und weitere (http://www.bmu.de/abfallwirtschaft/doc/1853.php), Internet access Nov. 2011 [90] Kaeb, H.: Biokunststoffe, Visionen und Investitionen, KUNSTSTOFFE 10/2011, S. 119 [91] N.N.: Pressrelease: Biokunststoffe knacken 2011 die 1-Millionen-Tonnen-Marke, European Bioplastics präsentiert neue Kapazitätsdaten auf der interpack, 12.5.2011 [92] Endres, H.-J., et al: Marktchancen, Flächenbedarf und zukünftige Entwicklungen, KUNSTSTOFFE 09/2011. S. 105ff [93] N.N.: Prognose von Plastics Europe, zitiert in Plastverarbeiter 2009 und Pressrelease of interpack 2011 [94] Shen, L; Haufe, J.; Patel, M.: Product overview and market projection of emerging biobased plastics, PRO-BIB Studie, Universiteit Utrecht, 2009 [95] N.N.: Häufig gestellte Fragen zur Nutzung von landwirtschaftlichen Ressourcen für die Produktion von Biokunststoffen (FAQ Mai 2011), European Bioplastics [96] Carus, M.: Land Use for bioplastics, bioplastics MAGAZINE, Vol. 4, Issue 04/09 [97] Endres, H.-J., A. Siebert-Raths, A.: Raw materials and arable land required for biopolymers, Bioplastics Magazine, Vol. 4, Issue 05/09

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[98] N.N.: Verpackung - Anforderungen an die Verwertung von Verpackungen durch Kompostierung und biologischen Abbau - Prüfschema und Bewertungskriterien für die Einstufung von Verpackungen, Deutsche Fassung EN 13432:2000

94 | 12 LIST OF REFERENCES

[99] N.N.: Kunststoffe - Bewertung der Kompostierbarkeit Prüfschema und Spezifikationen, Deutsche Fassung EN 14995:2006 [100] N.N.: ASTM D6400 - 04 Standard Specification for Compostable Plastics [101] N.N.: Fact Sheet: Was sind Biokunststoffe, Begriffe, Werkstofftypen und Technologien – Eine Einführung; European Bioplastics e.V., 2011 [102] N.N.: Logos Part 1: The “Compostable” logo of European Bioplastics (Basics); bioplastics MAGAZINE, Vol. 1, Issue 01/06 [103] N.N.: Logos Part 2: The “Compostable” logo of BPI: Biodegradable Products Institute, USA (Basics); bioplastics MAGAZINE, Vol. 1, Issue 02/06 [104] N.N.: Logos Part 3: The “OK Compost” logo of Vinçotte, Belgium (Basics); bioplastics MAGAZINE, Vol. 2, Issue 01/07 [105] N.N.: ASTM D6866: Standard Test Methods for Determining the Biobased Content of Solid, Liquid, and Gaseous Samples Using Radiocarbon Analysis [106] N.N.: www.yxy.com, Internet access, Jan 2012 [107]N.N.: Bioplastics: an important component of global sustainability, Biome bioplastics, White Paper, September 2011 [108] Müller, H.-M., Seebach, D.: Poly(hydroxyalkanoates): A Fifth Class of Physiologically Important Organic Biopolymers?

Angew. Chem. Int. Ed. Engl., 32, 477–502, 1993

Pictures

12

Photographs are either taken by the author or from iStockPhoto or fotalia (with a fee paid for), or the source is mentioned next to the photograph.

Graphics are either created by Mark Speckenbach or Julia Hunold (Polymedia Publisher Team) or the source is mentioned next to the graphic.

12 LIST OF REFERENCES | 95

13

INDEX

13

A accelerator pedal. . . . . . . . . . . . . 64 acrylic. . . . . . . . . . . . . . . . . . . . . . 39 AD . . . . . . . . . . . . . . . . . . . . . . . . 8, 71 additives . . . . . . . . . . . . . . . . 6, 31, 46 adhesive . . . . . . . . . . . . . . . . . . . . 66 adhesive tape. . . . . . . . . . . . . . . . 66 aerobic . . . . . . . . . . . . . . . . . . . . . . 8 agricultural land. . . . . . . . . . . . 43, 79 agriculture . . . . . . . . . . . . . . . . . . 59 amber. . . . . . . . . . . . . . . . . . . . . . 16 amylopectin . . . . . . . . . . . . . . . 12, 21 amylose. . . . . . . . . . . . . . . . . . . 12, 21 anaerobic . . . . . . . . . . . . . . . . . . . . 8 anaerobic digestion . . . . . . . . . . 8, 71 applications. . . . . . . . . . . . . . . . . . 56 artificial silk . . . . . . . . . . . . . . . . . 22 ASTM D6400. . . . . . . . . . . . . 9, 69, 82 ASTM D6866. . . . . . . . . . . . . . . 20, 83 automobile . . . . . . . . . . . . . . . . 31, 63 automotive . . . . . . . . . . . . . . . . 31, 63 B bacteria. . . . . . . . . . . . . . . . . . . . . . 8 beverage bottles. . . . . . . . . . . . . . 50 beverage cases. . . . . . . . . . . . . . . 50 biaxially oriented . . . . . . . . . . . 48, 66 biobased. . . . . . . . . . . . . . . . . . . . 83 biobased adhesives . . . . . . . . . . . 66 biobased content . . . . . . . . . . . . . 20 biobased plastics. . . . 7, 8, 10, 12, 16 biobased polyesters. . . . . . . . . . . 30 bio-BDO. . . . . . . . . . . . . . . 14, 36, 43 biodegradable plastics. . . . . . . . . . 7 bio-economy. . . . . . . . . . . . . . . . . 72 bioenergy . . . . . . . . . . . . . . . . . . . 43 bio-ethanol. . . . . . . . . . . . . . . . . . 15

96 | 13 INDEXS

biofuel. . . . . . . . . . . . . . . . . 11, 43, 70 biogas. . . . . . . . . . . . . . . . . . . . . . 70 biogasification. . . . . . . . . . . . . . . . 71 biomass. . . . . . . . . . . . . . . . . . . . . . 7 biomass content. . . . . . . . . . . . . . 20 bio-PDO. . . . . . . . . . . . . 14, 35, 42, 63 bioplastics. . . . . . . . . . . . . . . . . . 7, 12 bio-polyamides. . . . . . . . . . . . . . . 19 bio-polyethylene. . . . . . . . . . . . 15, 39 biopolymers . . . . . . . . . . . . . . . . . 12 bio-polypropylene. . . . . . . . . . . . . 41 BioPreferred. . . . . . . . . . . . . . . . . 83 bisphenol A. . . . . . . . . . . . . . . . . . 42 blends. . . . . . . . . . . . . . . . . . . . . . 19 blister . . . . . . . . . . . . . . . . . . . . 52, 56 blow moulding . . . . . . . . . . . . . . . 50 blown film extrusion. . . . . . . . . . . 48 bone screws. . . . . . . . . . . . . . . . . . 9 BoPLA. . . . . . . . . . . . . . . . . . . . 48, 66 bottles. . . . . . . . . . . . . . . . . 50, 56, 57 BPI. . . . . . . . . . . . . . . . . . . . . . . . . 82 breathing biofilm . . . . . . . . . . . . . 61 butanediol. . . . . . . . . . . . . . . . . . . 14 C CA . . . . . . . . . . . . . . . . . . . . . . . 17, 24 canisters. . . . . . . . . . . . . . . . . . . . 50 car bumpers. . . . . . . . . . . . . . . . . 50 carbohydrates. . . . . . . . . . . . . . . . 12 carbon. . . . . . . . . . . . . . . . . . . . . . . 8 carbon content. . . . . . . . . . . . . . . 20 carbon dioxide . . . . . . . . . . . . . . . . 7 carbon percentage. . . . . . . . . . . . 20 carpets . . . . . . . . . . . . . . . . 35, 63, 65 cascade recycling. . . . . . . . . . . . . 69 casein . . . . . . . . . . . . . . . . . 13, 17, 26 casting. . . . . . . . . . . . . . . . . . . . . . 54

cups. . . . . . . . . . . . . . . . . . . . . . . . 58 cutlery. . . . . . . . . . . . . . . . . 50, 58, 70 D D(-)lactic acid. . . . . . . . . . . . . . . . 30 dashboards. . . . . . . . . . . . . . . . 17, 31 desktop accessories. . . . . . . . . 31, 66 diisocyanates . . . . . . . . . . . . . . . . 38 dimethyl terephthalate. . . . . . . . . 32 DIN CERTCO. . . . . . . . . . . . . . . . . 82 disaccharides. . . . . . . . . . . . . . 12, 14 disposal. . . . . . . . . . . . . . . . . . . . . 58 door tread plates . . . . . . . . . . . . . 31 downcycling . . . . . . . . . . . . . . . . . 69 drinking cups . . . . . . . . . . . . . . . . 52 drop-in polymers . . . . . . . . . . . . . 19 drums. . . . . . . . . . . . . . . . . . . . . . 50 E ebony. . . . . . . . . . . . . . . . . . . . . . . 16 elastomers. . . . . . . . . . . 6, 24, 64, 66 EN 13432. . . . . . . . . . . . . . . . 9, 69, 82 EN 14855. . . . . . . . . . . . . . . . . . . . 69 EN 14995. . . . . . . . . . . . . . . . . . . . 82 End of Life. . . . . . . . . . . . . . . . . . . 68 energy recovery . . . . . . . . . . . . . . 70 engine compartment. . . . . . . . . . 64 enzymes . . . . . . . . . . . . . . . . . . . . . 8 EPDM . . . . . . . . . . . . . . . . . . . . . . 25 epoxy resins . . . . . . . . . . . . 41, 42, 74 ethylene. . . . . . . . . . . . . . . . . . . . . 15 ethylene glycol . . . . . . . . . . . . . . . 32 European Bioplastics. . . . . . 9, 72, 74 European Lead Markets Initiative.72 extrusion. . . . . . . . . . . . . . . . . . . . 47 extrusion blow moulding. . . . . . . 50 F fan housing. . . . . . . . . . . . . . . . . . 64 fatty acids. . . . . . . . . . . . . . . . . . . 12 fibres. . . . . . . . . . . . . . . . . . . . . . . 32 flat film. . . . . . . . . . . . . . . . . . . . . 48 13 INDEX | 97

13

castor oil. . . . . . . . . 14, 19, 37, 38, 64 catering. . . . . . . . . . . . . . . . . . . . . 58 CB. . . . . . . . . . . . . . . . . . . . . . . . . 24 cellophane . . . . . . . . . . . . . . . . . . 17 celluloid. . . . . . . . . . . . . . . . . . . 16, 23 cellulose. . . . . . . . . . . . . . . . . . 12, 22 cellulose acetate . . . . . . . . 17, 24, 54 cellulose butyrate. . . . . . . . . . . . . 24 cellulose derivatives. . . . . . . . . . . 23 cellulose ester . . . . . . . . . . . . . . . 23 cellulose ether. . . . . . . . . . . . . . . 23 cellulose hydrate . . . . . . . . . . . . . 16 cellulose nitrate. . . . . . . . . . . . . . 16 cellulose propionate. . . . . . . . . . . 24 cellulose regenerate . . . . . . . . . . 22 cellulose triacetate. . . . . . . . . . . . 17 chemical recycling. . . . . . . . . . . . 69 chitin. . . . . . . . . . . . . . . . . . . . . . . 12 chitosan. . . . . . . . . . . . . . . . . . . . . 12 chocolate box inserts. . . . . . . . . . 52 clamshell . . . . . . . . . . . . . . . . . . . 52 climate . . . . . . . . . . . . . . . . . . . . . 10 climate change. . . . . . . . . . . . . . . 10 climate neutral. . . . . . . . . . . . . . . 11 clips. . . . . . . . . . . . . . . . . . . . . . . . 59 closed loop. . . . . . . . . . . . . . . . . . 72 CO2. . . . . . . . . . . . . . . . . . . . . 7, 10, 82 coal . . . . . . . . . . . . . . . . . . . . . . . . . 8 cold incineration. . . . . . . . . . . . . . 69 collagen. . . . . . . . . . . . . . . . . . . . . 13 communal waste water. . . . . . . . 29 composting. . . . . . . . . . . . . . . . . 8, 69 compounding . . . . . . . . . . . . . . 31, 46 compressor nozzle. . . . . . . . . . . . 64 computer mouse . . . . . . . . . . . . . 62 consumer electronics . . . . . . . . . 62 coral . . . . . . . . . . . . . . . . . . . . . . . 16 cosmetics. . . . . . . . . . . . . . . . . . . 56 cotton cellulose . . . . . . . . . . . . . . 66 CP . . . . . . . . . . . . . . . . . . . . . . . . . 24 crystallinity. . . . . . . . . . . . . . . . . . 21 CTA . . . . . . . . . . . . . . . . . . . . . . . . 17

flax. . . . . . . . . . . . . . . . . . . . . . . . . 26 foam . . . . . . . . . . . . . . . . . . . . . 38, 52 foaming agents. . . . . . . . . . . . . . . 53 food production. . . . . . . . . . . . . . . 43 Ford. . . . . . . . . . . . . . . . . . . . . . . . 17 fossil resources . . . . . . . . . . 8, 10, 79 fructose. . . . . . . . . . . . . . . . . . . 12, 14 frying oil . . . . . . . . . . . . . . . . . . . . 44 fuel lines. . . . . . . . . . . . . . . . . . . . 64 fungi . . . . . . . . . . . . . . . . . . . . . . . . 8 G galalith . . . . . . . . . . . . . . . . . . . . . 17 garden furniture. . . . . . . . . . . . . . 50 gardening . . . . . . . . . . . . . . . . . . . 59 global warming. . . . . . . . . . . . . . . 10 glove-box lids. . . . . . . . . . . . . . . . 17 glucose. . . . . . . . . . . . . . . . . . . . . 14 glueing . . . . . . . . . . . . . . . . . . . . . 55 gluten . . . . . . . . . . . . . . . . . . . . . . 13 glycerine. . . . . . . . . . . . . . . . . . 17, 21 golf ball. . . . . . . . . . . . . . . . . . . . . 60 greenhouse gas . . . . . . . . . . . . . . 10 H hemp. . . . . . . . . . . . . . . . . . . . . . . 26 home compostable. . . . . . . . . . . . . 8 horn. . . . . . . . . . . . . . . . . . . . . . . . 16 horticulture. . . . . . . . . . . . . . . . . . 59 hunger. . . . . . . . . . . . . . . . . . . . . . 79 hygiene. . . . . . . . . . . . . . . . . . . . . 61 hygienic foil. . . . . . . . . . . . . . . . . . 49

13

I industrial composting . . . . . . . . . . 8 injection moulding. . . . . . . . . . . . 49 instrument panels. . . . . . . . . . . . 17 isoprene . . . . . . . . . . . . . . . . . . . . 64 ivory. . . . . . . . . . . . . . . . . . . . . . . . 16

98 | 13 INDEXS

J jerricans. . . . . . . . . . . . . . . . . . . . 50 joining plastic. . . . . . . . . . . . . . . . 55 K kenaf reinforcement. . . . . . . . . . . 63 keyboards. . . . . . . . . . . . . . . . . . . 62 L L(+)lactic acid. . . . . . . . . . . . . . . . 30 lactic acid. . . . . . . . . . . . . . . . . . . 14 lactide. . . . . . . . . . . . . . . . . . . . . . 30 land fill . . . . . . . . . . . . . . . . . . . . . 71 lapis lazuli. . . . . . . . . . . . . . . . . . . 16 latex. . . . . . . . . . . . . . . . . . . . . . 13, 24 Lead Markets Initiative. . . . . . . . . 72 lignin. . . . . . . . . . . . . . . . . . 12, 13, 26 linseed oil. . . . . . . . . . . . . . . . . . . 14 lipstick tubes . . . . . . . . . . . . . . 31, 61 loose fill. . . . . . . . . . . . . . . . . . . 21, 56 loudspeaker . . . . . . . . . . . . . . . . . 26 M mailing pouches. . . . . . . . . . . . . . 49 market. . . . . . . . . . . . . . . . . . . . 74, 78 market development . . . . . . . . . . 74 material recycling . . . . . . . . . . . . 68 meat trays. . . . . . . . . . . . . . . . . . . 52 medicine. . . . . . . . . . . . . . . . . . . . 61 methane . . . . . . . . . . . . . . . . . . . . 71 micro-organisms. . . . . . . . . . . . . . 8 mobile phone . . . . . . . . . . . . . . . . 62 monoethylene glycol . . . . . 19, 32, 43 monomers . . . . . . . . . . . . . . . . . . 14 monosaccharides. . . . . . . . . . . . . 14 mother of pearl. . . . . . . . . . . . . . . 16 mulch film. . . . . . . . . . . . . . . . . 59, 70 N nappies. . . . . . . . . . . . . . . . . . . 49, 61 natural fibres . . . . . . . . . . . . . . 26, 74

O oil price. . . . . . . . . . . . . . . . . . . . . 10 OK-Biobased. . . . . . . . . . . . . . . . . 83 oxo-degradable. . . . . . . . . . . . . . . . 9 P packaging chips. . . . . . . . . . . . . . 21 palm oil. . . . . . . . . . . . . . . . . . . . . 14 Parkesine. . . . . . . . . . . . . . . . . . . 16 partially biobased. . . . . . . . . . . . . 19 particle foam. . . . . . . . . . . . . . . 28, 54 PBAT. . . . . . . . . . . . . . . . . . . 9, 19, 21 PBS. . . . . . . . . . . . . . . . . . . . . . . 9, 36 PBSA. . . . . . . . . . . . . . . . . . . . . . 9, 36 PBT. . . . . . . . . . . . . . . . . . . . . . 35, 36 PC . . . . . . . . . . . . . . . . . . . . . . . . . 20 PE . . . . . . . . . . . . . . . . . . . . . . . . . 39 pedals. . . . . . . . . . . . . . . . . . . . . . 17 PEF . . . . . . . . . . . . . . . . . . . . . . . . 34 personal care. . . . . . . . . . . . . . . . 61 PET . . . . . . . . . . . . . . . . . . . . . . . . 19 petroleum. . . . . . . . . . . . . . . . . . 8, 10 petroleum boom. . . . . . . . . . . . . . 18 PHA. . . . . . . . . . . . . . . . . . . 18, 27, 66 PHB. . . . . . . . . . . . . . . . . . . . . . . . 28 PHV. . . . . . . . . . . . . . . . . . . . . . . . 28 PLA . . . . . . . . . . . . . 14, 18, 19, 30, 66 plant oils. . . . . . . . . . . . . . . . . . . . 14 plasticiser. . . . . . . . . . . . . . . . . . . 21 plastics. . . . . . . . . . . . . . . . . . . . . . 6 plastification. . . . . . . . . . . . . . . . . 46 plates. . . . . . . . . . . . . . . . . . . . . . . 58 polyacrylates. . . . . . . . . . . . . . . . . 39 polyamide. . . . . . . . . . . . . . . . . 36, 64 polybutylene adipate terephthalate.9, 19

polybutylene succinate. . . . . . . . 9, 36 polybutylene succinate adipate.9, 36 polybutylene terephthalate . . . 35, 36 polycarbonate. . . . . . . . . . . . . . . . 20 polyether block amide. . . . . . . . . 25 polyethylene . . . . . . . . . . . . . . . 15, 39 polyethylene terephthalate . . . . . 19 polyhydroxy butyrate. . . . . . . . . . . 28 polyhydroxy fatty acids. . . . . . . . . 27 polyhydroxy valerate. . . . . . . . . . . 28 polyhydroxyalkanoates. . . . . . . 13, 27 polylactic acid. . . . . . . . . . . . . . . . 30 polylactide. . . . . . . . . . . . . . . . . . . 30 polymers. . . . . . . . . . . . . . . . . . . . . 6 polyolefins. . . . . . . . . . . . . . . . . 19, 39 polyols. . . . . . . . . . . . . . . . . . . . . . 38 polypropylene. . . . . . . . . . . . . . . . 39 polypropylene terephthalate . . . . 63 polysaccharides. . . . . . . . . . . . . . 12 polysuccinates . . . . . . . . . . . . . . . 36 polytrimethylterephthalate . . . . . 35 polyurethane. . . . . . . . . 25, 38, 54, 74 polyvinyl alcohol. . . . . . . . . . . . . . 21 pouches. . . . . . . . . . . . . . . . . . . . . 56 PP . . . . . . . . . . . . . . . . . . . . . . . . . 39 propanediol. . . . . . . . . . . . . . . . . . 14 proteins. . . . . . . . . . . . . . . . 12, 13, 26 PTT . . . . . . . . . . . . . . . . . . . . . . . . 35 R radiocarbon method. . . . . . . . . 20, 83 rapeseed oil . . . . . . . . . . . . . . . 14, 64 rayon. . . . . . . . . . . . . . . . . . . . . . . 22 recyclate. . . . . . . . . . . . . . . . . . . . 68 recycling. . . . . . . . . . . . . . . . . . . . 68 refuse sacks. . . . . . . . . . . . . . . . . . 9 renewable resources. . . . . . . . . . . 7 resorbable. . . . . . . . . . . . . . . . . . . . 9 rotting fruit. . . . . . . . . . . . . . . . . . 70 RR. . . . . . . . . . . . . . . . . . . . . . . . . . 7 RRM. . . . . . . . . . . . . . . . . . . . . . . . . 7

13

natural gas. . . . . . . . . . . . . . . . . . . 8 natural polymers . . . . . . . . . . . . . 12 natural rubber . . . . . . . . . . . . . 13, 24 nets. . . . . . . . . . . . . . . . . . . . . . . . 56 nordic walking pole . . . . . . . . . . . 66

13 INDEX | 99

rubber. . . . . . . . . . . . . . . . . . . . 13, 24 runners. . . . . . . . . . . . . . . . . . . . . 68 S sand box . . . . . . . . . . . . . . . . . . . . 52 sand box toys . . . . . . . . . . . . . . . . 66 sea. . . . . . . . . . . . . . . . . . . . . . . . . 28 seat covers. . . . . . . . . . . . . . . . . . 63 sebacic acid . . . . . . . . . . . . 19, 37, 43 secondary raw material. . . . . . . . 68 seed strips . . . . . . . . . . . . . . . . . . 60 shampoo. . . . . . . . . . . . . . . . . . 50, 61 shopping bags . . . . . . . . . . 21, 49, 56 ski boots. . . . . . . . . . . . . . . . . . . . 66 soles of shoes. . . . . . . . . . . . . . . . 25 sorbitol . . . . . . . . . . . . . . . . . . . . . 21 soya. . . . . . . . . . . . . . . . . . . . . . . . 17 soya oil . . . . . . . . . . . . . . . . 14, 19, 38 starch . . . . . . . . . . . . . . . . . 12, 18, 21 Starch blends. . . . . . . . . . . . . . . . 21 steering wheels . . . . . . . . . . . . . . 17 stereocomplex . . . . . . . . . . . . . . . 31 succinic acid. . . . . . . . . . . . 14, 36, 43 sucrose. . . . . . . . . . . . . . . . . . . . . 14 sugar. . . . . . . . . . . . . . . . . . . . . 12, 14 sugar cane . . . . . . . . . . . . . . . . . . 15 sugar cane molasses. . . . . . . . . . 32 sun glasses. . . . . . . . . . . . . . . . . . 66 sunflower oil. . . . . . . . . . . . . . . . . 14 surgical thread. . . . . . . . . . . . . . . . 9 switchgrass. . . . . . . . . . . . . . . . . . 29

13

T tableware . . . . . . . . . . . . . . . . . . . 70 tanks. . . . . . . . . . . . . . . . . . . . . . . 50 terephthalic acid. . . . . . . . . 19, 32, 43 textiles. . . . . . . . . . . . . . . . . . . . . . 65 thermal recycling. . . . . . . . . . . . . 70 thermoforming. . . . . . . . . . . . . . . 52 thermoplastic elastomers. . . . . . 24 thermoplastic ether-ester elastomer.25

100 | 13 INDEXS

thermoplastic polyurethane . . . . 38 thermoplastic starch. . . . . . . . . . 21 thermoplastics. . . . . . . . . . . . . . . . 6 thermoset resins . . . . . . . . . 6, 41, 74 tobacco. . . . . . . . . . . . . . . . . . . . . 29 tooth-brush handles . . . . . . . . . . 25 tortoiseshell. . . . . . . . . . . . . . . . . 16 TPS . . . . . . . . . . . . . . . . . . . . . . . . 21 TPU. . . . . . . . . . . . . . . . . . . . . . . . 38 trash disposal. . . . . . . . . . . . . . . . . 8 trimmed edges of film. . . . . . . . . 68 trunk lid. . . . . . . . . . . . . . . . . . . . . 17 tubs. . . . . . . . . . . . . . . . . . . . . . . . 56 tubular film. . . . . . . . . . . . . . . . . . 48 twine. . . . . . . . . . . . . . . . . . . . . . . 59 tyres. . . . . . . . . . . . . . . . . . . . . . . . 64 U unsaturated polyester resin. . 41, 74 upholstery. . . . . . . . . . . . . . . . . . . 17 urn. . . . . . . . . . . . . . . . . . . . . . . . . 26 USDA. . . . . . . . . . . . . . . . . . . . . . . 84 V Vinรงotte. . . . . . . . . . . . . . . . . . . . . 82 viscose. . . . . . . . . . . . . . . . . . . . . . 22 W waste. . . . . . . . . . . . . . . . . . . . . . . 43 waste directives . . . . . . . . . . . . . . 82 waste water . . . . . . . . . . . . . . . . . 29 welding. . . . . . . . . . . . . . . . . . . . . 55 wheat. . . . . . . . . . . . . . . . . . . . . . . 17 wood flour. . . . . . . . . . . . . . . . . . . 74 wood pellets. . . . . . . . . . . . . . . . . 70 Y yoghurt cup. . . . . . . . . . . . . . . . . . 52

13 13 INDEX | 101

Bioplastics Basics, Applications, Market.

Petroleum is not an inexhaustible resource, and it is becoming ever more expensive. Burning of petroleum products (including plastics) has an impact on climate change. Bioplastics can offer an alternative in this regard.

Bioplastics are on the one hand biobased plastics (produced from renewable resources) and on the other hand may well be biodegradable plastics. Many bioplastics, but not all, meet both of these criteria. It is a widely held misconception that biobased plastics are automatically biodegradable, and vice versa.

This book offers a short introduction into plastics and bioplastics, explaining which renewable resources can be used to produce bioplastics, what types of bioplastic exist, and which ones are currently on the market.

Chapters on applications, the market, end-of-life scenarios, political background and regulations, and the outlook for plastics round off the book.

The author Dr. Michael Thielen ... is the founder and publisher of bioplastics MAGAZINE, the first and only trade publication solely dedicated to bioplastics. He is a qualified machinery design engineer with a degree in plastics technology from the RWTH University in Aachen. He has written several books on the subject of blow-moulding technology and disseminated his knowledge of plastics in numerous presentations, seminars, guest lectures and teaching assignments both inside and outside of Germany.

ISBN 978-3-9814981-1-0

polymedia publisher www.polymedia-publisher.com

BioPLAStICS Basics. Applications. Markets.

The book has deliberately been kept short but should nevertheless provide a comprehensive introduction to the subject of bioplastics.

Numerous literature references and Internet addresses will help the reader to look more deeply into any specific aspects.

BioPLAStICS Basics. applications.

Markets.

Michael Thielen