Plastic

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Household items made of various types of plastics Plastic household items.jpg
Household items made of various types of plastics

Plastics are a wide range of synthetic or semi-synthetic materials that use polymers as a main ingredient. Their plasticity makes it possible for plastics to be moulded, extruded or pressed into solid objects of various shapes. This adaptability, plus a wide range of other properties, such as being lightweight, durable, flexible, and inexpensive to produce, has led to its widespread use. Plastics typically are made through human industrial systems. Most modern plastics are derived from fossil fuel-based chemicals like natural gas or petroleum; however, recent industrial methods use variants made from renewable materials, such as corn or cotton derivatives. [1]

Contents

9.2 billion tonnes of plastic are estimated to have been made between 1950 and 2017, more than half of which has been produced since 2004. In 2020, 400 million tonnes of plastic were produced. [2] If global trends on plastic demand continue, it is estimated that by 2050 annual global plastic production will reach over 1.1 billion tonnes.

The success and dominance of plastics starting in the early 20th century has caused widespread environmental problems, [3] due to their slow decomposition rate in natural ecosystems. Most plastic produced has not been reused, or is incapable of reuse, either being captured in landfills or persisting in the environment as plastic pollution and microplastics. Plastic pollution can be found in all the world's major water bodies, for example, creating garbage patches in all of the world's oceans and contaminating terrestrial ecosystems. Of all the plastic discarded so far, some 14% has been incinerated and less than 10% has been recycled. [2]

In developed economies, about a third of plastic is used in packaging and roughly the same in buildings in applications such as piping, plumbing or vinyl siding. [4] Other uses include automobiles (up to 20% plastic [4] ), furniture, and toys. [4] In the developing world, the applications of plastic may differ; 42% of India's consumption is used in packaging. [4] In the medical field, polymer implants and other medical devices are derived at least partially from plastic. Worldwide, about 50 kg of plastic is produced annually per person, with production doubling every ten years.

The world's first fully synthetic plastic was Bakelite, invented in New York in 1907, by Leo Baekeland, [5] who coined the term "plastics". [6] Dozens of different types of plastics are produced today, such as polyethylene, which is widely used in product packaging, and polyvinyl chloride (PVC), used in construction and pipes because of its strength and durability. Many chemists have contributed to the materials science of plastics, including Nobel laureate Hermann Staudinger, who has been called "the father of polymer chemistry," and Herman Mark, known as "the father of polymer physics". [7]

Etymology

The word plastic derives from the Greek πλαστικός (plastikos) meaning "capable of being shaped or molded," and in turn from πλαστός (plastos) meaning "molded." [8] As a noun the word most commonly refers to the solid products of petrochemical-derived manufacturing. [9]

The noun plasticity refers specifically here to the deformability of the materials used in the manufacture of plastics. Plasticity allows molding, extrusion or compression into a variety of shapes: films, fibers, plates, tubes, bottles and boxes, among many others. Plasticity also has a technical definition in materials science outside the scope of this article referring to the non-reversible change in form of solid substances.

Structure

Most plastics contain organic polymers. [10] The vast majority of these polymers are formed from chains of carbon atoms, with or without the attachment of oxygen, nitrogen or sulfur atoms. These chains comprise many repeating units formed from monomers. Each polymer chain consists of several thousand repeating units. The backbone is the part of the chain that is on the main path, linking together a large number of repeat units. To customize the properties of a plastic, different molecular groups called side chains hang from this backbone; they are usually hung from the monomers before the monomers themselves are linked together to form the polymer chain. The structure of these side chains influences the properties of the polymer.

Properties and classifications

Plastics are usually classified by the chemical structure of the polymer's backbone and side chains. Important groups classified in this way include the acrylics, polyesters, silicones, polyurethanes, and halogenated plastics. Plastics can be classified by the chemical process used in their synthesis, such as condensation, polyaddition, and cross-linking. [11] They can also be classified by their physical properties, including hardness, density, tensile strength, thermal resistance, and glass transition temperature. Plastics can additionally be classified by their resistance and reactions to various substances and processes, such as exposure to organic solvents, oxidation, and ionizing radiation. [12] Other classifications of plastics are based on qualities relevant to manufacturing or product design for a particular purpose. Examples include thermoplastics, thermosets, conductive polymers, biodegradable plastics, engineering plastics and elastomers.

Thermoplastics and thermosetting polymers

A plastic handle from a kitchen utensil, deformed by heat and partially melted Melted plastic.jpg
A plastic handle from a kitchen utensil, deformed by heat and partially melted

One important classification of plastics is the degree to which the chemical processes used to make them are reversible or not.

Thermoplastics do not undergo chemical change in their composition when heated and thus can be molded repeatedly. Examples include polyethylene (PE), polypropylene (PP), polystyrene (PS), and polyvinyl chloride (PVC). [13]

Thermosets, or thermosetting polymers, can melt and take shape only once: after they have solidified, they stay solid. [14] If reheated, thermosets decompose rather than melt. In the thermosetting process, an irreversible chemical reaction occurs. The vulcanization of rubber is an example of this process. Before heating in the presence of sulfur, natural rubber (polyisoprene) is a sticky, slightly runny material; after vulcanization, the product is dry and rigid.

Amorphous plastics and crystalline plastics

Many plastics are completely amorphous (without a highly ordered molecular structure), [15] including thermosets, polystyrene, and methyl methacrylate (PMMA). Crystalline plastics exhibit a pattern of more regularly spaced atoms, such as high-density polyethylene (HDPE), polybutylene terephthalate (PBT), and polyether ether ketone (PEEK). However, some plastics are partially amorphous and partially crystalline in molecular structure, giving them both a melting point and one or more glass transitions (the temperature above which the extent of localized molecular flexibility is substantially increased). These so-called semi-crystalline plastics include polyethylene, polypropylene, polyvinyl chloride, polyamides (nylons), polyesters and some polyurethanes.

Conductive polymers

Intrinsically Conducting Polymers (ICP) are organic polymers that conduct electricity. While a conductivity of up to 80 kS/cm in stretch-oriented polyacetylene, [16] has been achieved, it does not approach that of most metals. For example, copper has a conductivity of several hundred kS/cm. [17]

Biodegradable plastics and bioplastics

Biodegradable plastics

Biodegradable plastics are plastics that degrade (break down) upon exposure to sunlight or ultra-violet radiation; water or dampness; bacteria; enzymes; or wind abrasion. Attack by insects, such as waxworms and mealworms, can also be considered as forms of biodegradation. Aerobic degradation requires that the plastic be exposed at the surface, whereas anaerobic degradation would be effective in landfill or composting systems. Some companies produce biodegradable additives to enhance biodegradation. Although starch powder can be added as a filler to allow some plastics to degrade more easily, such treatment does not lead to complete breakdown. Some researchers have genetically engineered bacteria to synthesize completely biodegradable plastics, such as polyhydroxy butyrate (PHB); however, these are relatively costly as of 2021. [18]

Bioplastics

While most plastics are produced from petrochemicals, bioplastics are made substantially from renewable plant materials like cellulose and starch. [19] Due both to the finite limits of fossil fuel reserves and to rising levels of greenhouse gases caused primarily by the burning of those fuels, the development of bioplastics is a growing field. [20] [21] Global production capacity for bio-based plastics is estimated at 327,000 tonnes per year. In contrast, global production of polyethylene (PE) and polypropylene (PP), the world's leading petrochemical-derived polyolefins, was estimated at over 150 million tonnes in 2015. [22]

Plastic industry

The plastic industry includes the global production, compounding, conversion and sale of plastic products. Although the Middle East and Russia produce most of the required petrochemical raw materials, the production of plastic is concentrated in the global East and West. The plastic industry comprises a huge number of companies and can be divided into several sectors:

Production

Between 1950 and 2017, 9.2 billion tonnes of plastic are estimated to have been made, with more than half this having been produced since 2004. Since the birth of the plastic industry in the 1950s, global production has increased enormously, reaching 400 million tonnes a year in 2021; this is up from 381 million metric tonnes in 2015 (excluding additives). [2] [23] From the 1950s, rapid growth occurred in the use of plastics for packaging, in building and construction, and in other sectors. [2] If global trends on plastic demand continue, it is estimated that by 2050 annual global plastic production will exceed 1.1 billion tonnes annually. [2]

Polypropylene plants
Slovnaft - new polypropylene plant PP3.JPG
A Slovnaft facility in Bratislava, Slovakia
Ilham Aliyev, Italian President Sergio Mattarella attended inauguration of polypropylene plant constructed in Sumgayit Chemical Industrial Park under SOCAR Polymer project 32.jpg
A SOCAR Polymer polypropylene plant in Sumgayit, Azerbaijan
Annual global plastic production 1950–2015. [23] Vertical lines denote the 1973–1975 recession and the financial crisis of 2007–2008 which caused brief lowering of plastic production.

Plastics are produced in chemical plants by the polymerization of their starting materials (monomers); which are almost always petrochemical in nature. Such facilities are normally large and are visually similar to oil refineries, with sprawling pipework running throughout. The large size of these plants allows them to exploit economies of scale. Despite this, plastic production is not particularly monopolized, with about 100 companies accounting for 90% of global production. [24] This includes a mixture of private and state-owned enterprises. Roughly half of all production takes place in East Asia, with China being the largest single producer. Major international producers include:

Global plastic production (2020) [25]
RegionGlobal production
China31%
Japan3%
Rest of Asia17%
NAFTA 19%
Latin America4%
Europe16%
CIS 3%
Middle East & Africa7%

Historically, Europe and North America have dominated global plastics production. However, since 2010 Asia has emerged as a significant producer, with China accounting for 31% of total plastic resin production in 2020. [25] Regional differences in the volume of plastics production are driven by user demand, the price of fossil fuel feedstocks, and investments made in the petrochemical industry. For example, since 2010 over US$200 billion has been invested in the United States in new plastic and chemical plants, stimulated by the low cost of raw materials. In the European Union (EU), too, heavy investments have been made in the plastics industry, which employs over 1.6 million people with a turnover of more than 360 billion euros per year. In China in 2016 there were over 15,000 plastic manufacturing companies, generating more than US$366 billion in revenue. [2]

In 2017, the global plastics market was dominated by thermoplastics– polymers that can be melted and recast. Thermoplastics include polyethylene (PE), polyethylene terephthalate (PET), polypropylene (PP), polyvinyl chloride (PVC), polystyrene (PS) and synthetic fibres, which together represent 86% of all plastics. [2]

Compounding

Plastic compounding scheme for a thermosoftening material Compounding-en.png
Plastic compounding scheme for a thermosoftening material

Plastic is not sold as a pure unadulterated substance, but is instead mixed with various chemicals and other materials, which are collectively known as additives. These are added during the compounding stage and include substances such as stabilizers, plasticizers and dyes, which are intended to improve the lifespan, workability or appearance of the final item. In some cases, this can involve mixing different types of plastic together to form a polymer blend, such as high impact polystyrene. Large companies may do their own compounding prior to production, but some producers have it done by a third party. Companies that specialize in this work are known as Compounders.

The compounding of thermosetting plastic is relatively straightforward; as it remains liquid until it is cured into its final form. For thermosoftening materials, which are used to make the majority of products, it is necessary to melt the plastic in order to mix-in the additives. This involves heating it to anywhere between 150–320 °C (300–610 °F). Molten plastic is viscous and exhibits laminar flow, leading to poor mixing. Compounding is therefore done using extrusion equipment, which is able to supply the necessary heat and mixing to give a properly dispersed product.

The concentrations of most additives are usually quite low, however high levels can be added to create Masterbatch products. The additives in these are concentrated but still properly dispersed in the host resin. Masterbatch granules can be mixed with cheaper bulk polymer and will release their additives during processing to give a homogeneous final product. This can be cheaper than working with a fully compounded material and is particularly common for the introduction of colour.

Converting

Short video on injection molding (9 min 37 s)
Blow molding process.jpg
Blow molding a plastic drinks bottle

Companies that produce finished goods are known as converters (sometimes processors). The vast majority of plastics produced worldwide are thermosoftening and must be heated until molten in order to be molded. Various sorts of extrusion equipment exist which can then form the plastic into almost any shape.

For thermosetting materials the process is slightly different, as the plastics are liquid to begin with and but must be cured to give solid products, but much of the equipment is broadly similar.

The most commonly produced plastic consumer products include packaging made from LDPE (e.g. bags, containers, food packaging film), containers made from HDPE (e.g. milk bottles, shampoo bottles, ice cream tubs), and PET (e.g. bottles for water and other drinks). Together these products account for around 36% of plastics use in the world. Most of them (e.g. disposable cups, plates, cutlery, takeaway containers, carrier bags) are used for only a short period, many for less than a day. The use of plastics in building and construction, textiles, transportation and electrical equipment also accounts for a substantial share of the plastics market. Plastic items used for such purposes generally have longer life spans. They may be in use for periods ranging from around five years (e.g. textiles and electrical equipment) to more than 20 years (e.g. construction materials, industrial machinery). [2]

Plastic consumption differs among countries and communities, with some form of plastic having made its way into most people's lives. North America (i.e. the North American Free Trade Agreement or NAFTA region) accounts for 21% of global plastic consumption, closely followed by China (20%) and Western Europe (18%). In North America and Europe there is high per capita plastic consumption (94 kg and 85 kg/capita/year, respectively). In China there is lower per capita consumption (58 kg/capita/year), but high consumption nationally because of its large population. [2]

Types of plastics

Commodity plastics

Chemical structures and uses of some common plastics Plastics Summary.svg
Chemical structures and uses of some common plastics

Around 70% of global production is concentrated in six major polymer types, the so-called commodity plastics. Unlike most other plastics these can often be identified by their resin identification code (RIC):

Symbol Resin Code 01 PET.svg Polyethylene terephthalate (PET or PETE)
Symbol Resin Code 02 PE-HD.svg High-density polyethylene (HDPE or PE-HD)
Symbol Resin Code 03 PVC.svg Polyvinyl chloride (PVC or V)
Symbol Resin Code 04 PE-LD.svg Low-density polyethylene (LDPE or PE-LD),
Symbol Resin Code 05 PP.svg Polypropylene (PP)
Symbol Resin Code 06 PS.svg Polystyrene (PS)

Polyurethanes (PUR) and PP&A fibres [26] are often also included as major commodity classes, although they usually lack RICs, as they are chemically quite diverse groups. These materials are inexpensive, versatile and easy to work with, making them the preferred choice for the mass production everyday objects. Their biggest single application is in packaging, with some 146 million tonnes being used this way in 2015, equivalent to 36% of global production. Due to their dominance; many of the properties and problems commonly associated with plastics, such as pollution stemming from their poor biodegradability, are ultimately attributable to commodity plastics.

A huge number of plastics exist beyond the commodity plastics, with many having exceptional properties.

Global plastic production by polymer type (2015) [23]
PolymerProduction (Mt)Percentage of all plasticsPolymer typeThermal character
Low-density polyethylene (LDPE)6415.7%PolyolefinThermoplastic
High-density polyethylene (HDPE)5212.8%PolyolefinThermoplastic
polypropylene (PP)6816.7%PolyolefinThermoplastic
Polystyrene (PS)256.1%Unsaturated polyolefinThermoplastic
Polyvinyl chloride (PVC)389.3%HalogenatedThermoplastic
Polyethylene terephthalate (PET)338.1%CondensationThermoplastic
Polyurethane (PUR)276.6%CondensationThermoset [27]
PP&A Fibers [26] 5914.5%CondensationThermoplastic
All Others163.9%VariousVaries
Additives256.1%--
Total407100%--

Engineering plastics

Engineering plastics are more robust and are used to make products such as vehicle parts, building and construction materials, and some machine parts. In some cases they are polymer blends formed by mixing different plastics together (ABS, HIPS etc.). Engineering plastics can replace metals in vehicles, lowering their weight and improving fuel efficiency by 6–8%. Roughly 50% of the volume of modern cars is made of plastic, but this only accounts for 12–17% of the vehicle weight. [28]

High-performance plastics

High-performance plastics are usually expensive, with their use limited to specialised applications which make use of their superior properties.

Applications

The largest application for plastics is as packaging materials, but they are used in a wide range of other sectors, including: construction (pipes, gutters, door and windows), textiles (stretchable fabrics, fleece), consumer goods (toys, tableware, toothbrushes), transportation (headlights, bumpers, body panels, wing mirrors), electronics (phones, computers, televisions) and as machine parts. [23]



Additives

Additives are chemicals blended into plastics to change their performance or appearance, making it possible to alter the properties of plastics to better suit their intended applications. [31] [32] Additives are therefore one of the reasons why plastic is used so widely. [33] Plastics are composed of chains of polymers. Many different chemicals are used as plastic additives. A randomly chosen plastic product generally contains around 20 additives. The identities and concentrations of additives are generally not listed on products. [2]

In the EU, over 400 additives are used in high volumes. [34] [2] 5500 additives were found in a global market analysis. [35] At a minimum all plastic contains some polymer stabilisers which permit them to be melt-processed (moulded) without suffering polymer degradation. Other additives are optional and can be added as required, with loadings varying significantly between applications. The amount of additives contained in plastics varies depending on the additives’ function. For example, additives in polyvinyl chloride (PVC) can constitute up to 80% of the total volume. [2] Pure unadulterated plastic (barefoot resin) is never sold, even by the primary producers.

Leaching

Additives may be weakly bound to the polymers or react in the polymer matrix. Although additives are blended into plastic they remain chemically distinct from it, and can gradually leach back out during normal use, when in landfills, or following improper disposal in the environment. [36] Additives may also degrade to form other toxic molecules. Plastic fragmentation into microplastics and nanoplastics can allow chemical additives to move in the environment far from the point of use. Once released, some additives and derivatives may persist in the environment and bioaccumulate in organisms. They can have adverse effects on human health and biota. A recent review by the United States Environmental Protection Agency (US EPA) revealed that out of 3,377 chemicals potentially associated with plastic packaging and 906 likely associated with it, 68 were ranked by ECHA as "highest for human health hazards" and 68 as "highest for environmental hazards". [2]

Recycling

As additives change the properties of plastics they have to be considered during recycling. Presently, almost all recycling is performed by simply remelting and reforming used plastic into new items. Additives present risks in recycled products, as they are difficult to remove. When plastic products are recycled, it is highly likely that the additives will be integrated into the new products. Waste plastic, even if it is all of the same polymer type, will contain varying types and amounts of additives. Mixing these together can give a material with inconsistent properties, which can be unappealing to industry. For example, mixing different coloured plastics with different plastic colorants together can produce a discoloured or brown material and for this reason plastic is usually sorted by both polymer type and color before recycling. [2]

Absence of transparency and reporting across the value chain often results in lack of knowledge concerning the chemical profile of the final products. For example, products containing brominated flame retardants have been incorporated into new plastic products. Flame retardants are a group of chemicals used in electronic and electrical equipment, textiles, furniture and construction materials which should not be present in food packaging or child care products. A recent study found brominated dioxins as unintentional contaminants in toys made from recycled plastic electronic waste that contained brominated flame retardants. Brominated dioxins have been found to exhibit toxicity similar to that of chlorinated dioxins. They can have negative developmental effects and negative effects on the nervous system and interfere with mechanisms of the endocrine system. [2]

Health effects

Many of the controversies associated with plastics actually relate to their additives, as some compounds can be persistent, bioaccumulating and potentially harmful. [37] [38] [31] The now banned flame retardants OctaBDE and PentaBDE are an example of this, while the health effects of phthalates are an ongoing area of public concern. Additives can also be problematic if waste is burned, especially when burning is uncontrolled or takes place in low- technology incinerators, as is common in many developing countries. Incomplete combustion can cause emissions of hazardous substances such as acid gases and ash which can contain persistent organic pollutants (POPs) such as dioxins. [2]

A number of additives identified as hazardous to humans and/or the environment are regulated internationally. The Stockholm Convention on Persistent Organic Pollutants (POPs) is a global treaty to protect human health and the environment from chemicals that remain intact in the environment for long periods, become widely distributed geographically, accumulate in the fatty tissue of humans and wildlife, and have harmful impacts on human health or on the environment. [2]

Other additives proven to be harmful such as cadmium, chromium, lead and mercury (regulated under the Minamata Convention on Mercury), which have previously been used in plastic production, are banned in many jurisdictions. However they are still routinely found in some plastic packaging including food packaging. The use of the additive bisphenol A (BPA) in plastic baby bottles is banned in many parts of the world, but is not restricted in some low-income countries. [2]

In 2023, plasticosis, a new disease caused solely by plastics, was discovered in seabirds. The birds identified as having the disease have scarred digestive tracts from ingesting plastic waste. [39] "When birds ingest small pieces of plastic, they found, it inflames the digestive tract. Over time, the persistent inflammation causes tissues to become scarred and disfigured, affecting digestion, growth and survival." [40]

Types of additive

Additive typeTypical concentration when present (%) [31] DescriptionExample compoundsCommentShare of global additive production (by weight) [23]
Plasticizers 10–70Plastics can be brittle, adding some plasticizer makes them more durable, adding lots makes them flexible Phthalates are the dominant class, safer alternatives include adipate esters (DEHA, DOA) and citrate esters (ATBC and TEC)80–90% of world production is used in PVC, much of the rest is used in cellulose acetate. For most products loadings are between 10 and 35%, high loadings are used for plastisols 34%
Flame retardants 1–30Being petrochemicals, most plastics burn readily, flame retardants can prevent this Brominated flame retardants, chlorinated paraffins Non-chlorinated organophosphates are ecologically safer, though often less efficient13%
Heat stabilizers 0.3-5Prevents heat related degradationTraditionally derivatives of lead, cadmium & tin. Safer modern alternatives include barium/zinc mixtures and calcium stearate, along with various synergistsAlmost exclusively used in PVC.5%
Fillers 0–50Bulking agents. Can change appearance and mechanical properties, can lower price Calcium carbonate "chalk", talc, glass beads, carbon black. Also reinforcing fillers like carbon-fiber Most opaque plastic contains fillers. High levels can also protect against UV rays.28%
Impact modifiers10–40Improved toughness and resistance to damage [41] Typically some other elastomeric polymer, e.g. rubbers, styrene copolymers Chlorinated polyethylene is used for PVC5%
Antioxidants 0.05–3Protects against degradation during processing Phenols, phosphite esters, certain thioethers The most widely used type of additives, all plastics will contain polymer stabilisers of some sort6%
Colorants 0.001-10Imparts colourNumerous dyes or pigments2%
Lubricants 0.1-3Assist in forming/molding the plastic, includes processing aids (or flow aids), release agents, slip additivesHazardous PFASs. Paraffin wax, wax esters, metal stearates (i.e. zinc stearate), long-chain fatty acid amides (oleamide, erucamide)Very common. All examples form a coating between the plastic and machine parts during production. Reduces pressure and power usage in the extruder. Reduces imperfections.2%
Light stabilizers 0.05–3Protects against UV damage HALS, UV blockers and quenchersNormally only used for items intended for outdoor use1%
OtherVariousAntimicrobials, antistatics, blowing agents, nucleating agents, clarifying agents4%

Toxicity

Pure plastics have low toxicity due to their insolubility in water, and because they have a large molecular weight, they are biochemically inert. Plastic products contain a variety of additives, however, some of which can be toxic. [42] For example, plasticizers like adipates and phthalates are often added to brittle plastics like PVC to make them pliable enough for use in food packaging, toys, and many other items. Traces of these compounds can leach out of the product. Owing to concerns over the effects of such leachates, the EU has restricted the use of DEHP (di-2-ethylhexyl phthalate) and other phthalates in some applications, and the US has limited the use of DEHP, DPB, BBP, DINP, DIDP, and DnOP in children's toys and child-care articles through the Consumer Product Safety Improvement Act. Some compounds leaching from polystyrene food containers have been proposed to interfere with hormone functions and are suspected human carcinogens (cancer-causing substances). [43] Other chemicals of potential concern include alkylphenols. [38]

While a finished plastic may be non-toxic, the monomers used in the manufacture of its parent polymers may be toxic. In some cases, small amounts of those chemicals can remain trapped in the product unless suitable processing is employed. For example, the World Health Organization's International Agency for Research on Cancer (IARC) has recognized vinyl chloride, the precursor to PVC, as a human carcinogen. [43]

Bisphenol A (BPA)

Some plastic products degrade to chemicals with estrogenic activity. [44] The primary building block of polycarbonates, bisphenol A (BPA), is an estrogen-like endocrine disruptor that may leach into food. [43] Research in Environmental Health Perspectives finds that BPA leached from the lining of tin cans, dental sealants and polycarbonate bottles can increase the body weight of lab animals' offspring. [45] A more recent animal study suggests that even low-level exposure to BPA results in insulin resistance, which can lead to inflammation and heart disease. [46] As of January 2010, the Los Angeles Times reported that the US Food and Drug Administration (FDA) is spending $30 million to investigate indications of BPA's link to cancer. [47] Bis(2-ethylhexyl) adipate, present in plastic wrap based on PVC, is also of concern, as are the volatile organic compounds present in new car smell. The EU has a permanent ban on the use of phthalates in toys. In 2009, the US government banned certain types of phthalates commonly used in plastic. [48]

Environmental effects

A communication campaign infographic showing that there will be more plastic in the oceans than fish by 2050 More Plastic in the Ocean than Fish Infographic.png
A communication campaign infographic showing that there will be more plastic in the oceans than fish by 2050

Because the chemical structure of most plastics renders them durable, they are resistant to many natural degradation processes. Much of this material may persist for centuries or longer, given the demonstrated persistence of structurally similar natural materials such as amber.

There are differing estimates of how much plastic waste has been produced in the last century. By one estimate, one billion tons of plastic waste have been discarded since the 1950s. [49] Others estimate a cumulative human production of 8.3 billion tons of plastic, of which 6.3 billion tons is waste, with only 9% getting recycled. [50]

It is estimated that this waste is made up of 81% polymer resin, 13% polymer fibres and 32% additives. In 2018 more than 343 million tonnes of plastic waste were generated, 90% of which was composed of post-consumer plastic waste (industrial, agricultural, commercial and municipal plastic waste). The rest was pre-consumer waste from resin production and manufacturing of plastic products (e.g. materials rejected due to unsuitable colour, hardness, or processing characteristics). [2]

The Ocean Conservancy reported that China, Indonesia, Philippines, Thailand, and Vietnam dump more plastic into the sea than all other countries combined. [51] The rivers Yangtze, Indus, Yellow, Hai, Nile, Ganges, Pearl, Amur, Niger, and Mekong "transport 88% to 95% of the global [plastics] load into the sea." [52] [53] [ verify quote punctuation ]

The presence of plastics, particularly microplastics, within the food chain is increasing. In the 1960s microplastics were observed in the guts of seabirds, and since then have been found in increasing concentrations. [54] The long-term effects of plastics in the food chain are poorly understood. In 2009 it was estimated that 10% of modern waste was plastic, [55] although estimates vary according to region. [54] Meanwhile, 50% to 80% of debris in marine areas is plastic. [54] Plastic is often used in agriculture. There is more plastic in the soil than in the oceans. The presence of plastic in the environment hurts ecosystems and human health. [56]

Research on the environmental impacts has typically focused on the disposal phase. However, the production of plastics is also responsible for substantial environmental, health and socioeconomic impacts. [57]

Prior to the Montreal Protocol, CFCs had been commonly used in the manufacture of the plastic polystyrene, the production of which had contributed to depletion of the ozone layer.

Efforts to minimize environmental impact of plastics may include lowering of plastics production and use, waste- and recycling-policies, and the proactive development and deployment of alternatives to plastics such as for sustainable packaging.

Microplastics

Microplastics in sediments from four rivers in Germany. Note the diverse shapes indicated by white arrowheads. (The white bars represent 1 mm for scale.) Microplastics in sediments.jpg
Microplastics in sediments from four rivers in Germany. Note the diverse shapes indicated by white arrowheads. (The white bars represent 1 mm for scale.)
Photodegraded Plastic Straw. A light touch breaks larger straw into microplastics.

Microplastics are fragments of any type of plastic less than 5 mm (0.20 in) in length, [58] according to the U.S. National Oceanic and Atmospheric Administration (NOAA) [59] [60] and the European Chemicals Agency. [61] They cause pollution by entering natural ecosystems from a variety of sources, including cosmetics, clothing, food packaging, and industrial processes. [58] [62]

The term macroplastics is used to differentiate microplastics from larger plastic waste, such as plastic bottles or bigger pieces of plastics. Two classifications of microplastics are currently recognized. Primary microplastics include any plastic fragments or particles that are already 5.0 mm in size or less before entering the environment. [62] These include microfibers from clothing, microbeads, plastic glitter [63] and plastic pellets (also known as nurdles). [64] [65] [66] Secondary microplastics arise from the degradation (breakdown) of larger plastic products through natural weathering processes after entering the environment. [62] Such sources of secondary microplastics include water and soda bottles, fishing nets, plastic bags, microwave containers, tea bags and tire wear. [67] [66] [68] [69] Both types are recognized to persist in the environment at high levels, particularly in aquatic and marine ecosystems, where they cause water pollution. [70] 35% of all ocean microplastics come from textiles/clothing, primarily due to the erosion of polyester, acrylic, or nylon-based clothing, often during the washing process. [71] However, microplastics also accumulate in the air and terrestrial ecosystems.

Because plastics degrade slowly (often over hundreds to thousands of years), [72] [73] microplastics have a high probability of ingestion, incorporation into, and accumulation in the bodies and tissues of many organisms. [58] The toxic chemicals that come from both the ocean and runoff can also biomagnify up the food chain. [74] [75] In terrestrial ecosystems, microplastics have been demonstrated to reduce the viability of soil ecosystems and reduce weight of earthworms. [76] [77] The cycle and movement of microplastics in the environment are not fully known, but research is currently underway to investigate the phenomenon. [62] Deep layer ocean sediment surveys in China (2020) show the presence of plastics in deposition layers far older than the invention of plastics, leading to suspected underestimation of microplastics in surface sample ocean surveys. [78] Microplastics have also been found in the high mountains, at great distances from their source. [79]

Microplastics have also been found in human blood, though their effects are largely unknown. [80]

Decomposition of plastics

Plastics degrade by a variety of processes, the most significant of which is usually photo-oxidation. Their chemical structure determines their fate. Polymers' marine degradation takes much longer as a result of the saline environment and cooling effect of the sea, contributing to the persistence of plastic debris in certain environments. [54] Recent studies have shown, however, that plastics in the ocean decompose faster than had been previously thought, due to exposure to the sun, rain, and other environmental conditions, resulting in the release of toxic chemicals such as bisphenol A. However, due to the increased volume of plastics in the ocean, decomposition has slowed down. [81] The Marine Conservancy has predicted the decomposition rates of several plastic products: It is estimated that a foam plastic cup will take 50 years, a plastic beverage holder will take 400 years, a disposable diaper will take 450 years, and fishing line will take 600 years to degrade. [82]

Microbial species capable of degrading plastics are known to science, some of which are potentially useful for disposal of certain classes of plastic waste.

Manual material triage for recycling TriagemDeLixo.jpg
Manual material triage for recycling

Recycling

Plastic recycling
Municipal recycling facilities, Montgomery County, MD. 2007, Credit USEPA (14410405277).jpg
Bales of PET bottles stacked.jpg
Watering can made from 12 recycled bottles, Intratuin Winschoten (2020) 01.jpg
Aglomerat PVD.JPG
Clockwise from top left:
  • Sorting plastic waste at a single-stream recycling centre
  • Baled colour-sorted used bottles
  • Recovered HDPE ready for recycling
  • A watering can made from recycled bottles

Plastic recycling is the processing of plastic waste into other products. [103] [104] [105] Recycling can reduce dependence on landfill, conserve resources and protect the environment from plastic pollution and greenhouse gas emissions. [106] [107] Recycling rates lag those of other recoverable materials, such as aluminium, glass and paper. From the start of production through to 2015, the world produced some 6.3 billion tonnes of plastic waste, only 9% of which has been recycled, and only ~1% has been recycled more than once. [108] Of the remaining waste, 12% was incinerated and 79% either sent to landfill or lost into the environment as pollution. [108]

Almost all plastic is non-biodegradable and without recycling, spreads across the environment [109] [110] where it can cause harm. For example, as of 2015 approximately 8 million tons of waste plastic enter the oceans annually, damaging the ecosystem and forming ocean garbage patches. [111] Even the highest quality recycling processes lead to substantial plastic waste during the sorting and cleaning process, releasing large amounts of microplastics in waste water, and dust from the process. [112] [113]

Almost all recycling is mechanical: melting and reforming plastic into other items. This can cause polymer degradation at a molecular level, and requires that waste be sorted by colour and polymer type before processing, which is complicated and expensive. Errors can lead to material with inconsistent properties, rendering it unappealing to industry. [114] In feedstock recycling, waste plastic is converted into its starting chemicals, which can then become fresh plastic. This involves higher energy and capital costs. Alternatively, plastic can be burned in place of fossil fuels, in energy recovery facilities or biochemically converted into other useful chemicals for industry. In some countries, burning is the dominant form of plastic waste disposal, particularly where landfill diversion policies are in place.

Plastic recycling is low in the waste hierarchy. It has been advocated since the early 1970s, [115] but due to economic and technical challenges, did not impact plastic waste to any significant extent until the late 1980s. The plastics industry has been criticised for lobbying for expansion of recycling programs, even while research showed that most plastic could not be economically recycled. [116] [117] [118]

Pyrolysis

By heating to above 500 °C in the absence of oxygen (pyrolysis), plastics can be broken down into simpler hydrocarbons. These can be reused as starting materials for new plastics. [119] They can also be used as fuels. [120]

Climate change

According to the OECD, plastic contributed greenhouse gases in the equivalent of 1.8 billion tons of carbon dioxide (CO2) to the atmosphere in 2019, 3.4% of global emissions. [121] They say that by 2060, plastic could emit 4.3 billion tons of greenhouse gas emissions a year.

The effect of plastics on global warming is mixed. Plastics are generally made from fossil gas or petroleum, thus the production of plastics creates further fugitive emissions of methane when the fossil gas or petroleum is produced. Also much of the energy used in plastic production is not sustainable energy, for example high temperature from burning fossil gas. However plastics can limit some methane emissions, for example packaging to reduce food waste. [122]

Production of plastics

Production of plastics from crude oil requires 7.9 to 13.7 kWh/lb (taking into account the average efficiency of US utility stations of 35%). Producing silicon and semiconductors for modern electronic equipment is even more energy consuming: 29.2 to 29.8 kWh/lb for silicon, and about 381 kWh/lb for semiconductors. [123] This is much higher than the energy needed to produce many other materials. For example, to produce iron (from iron ore) requires 2.5-3.2 kWh/lb of energy; glass (from sand, etc.) 2.3–4.4 kWh/lb; steel (from iron) 2.5–6.4 kWh/lb; and paper (from timber) 3.2–6.4 kWh/lb. [124]

Incineration of plastics

Quickly burning plastics at very high temperatures breaks down many toxic components, such as dioxins and furans. This approach is widely used in municipal solid waste incineration. Municipal solid waste incinerators also normally treat the flue gas to decrease pollutants further, which is needed because uncontrolled incineration of plastic produces carcinogenic polychlorinated dibenzo-p-dioxins. [125] Open-air burning of plastic occurs at lower temperatures and normally releases such toxic fumes.

In the European Union, municipal waste incineration is regulated by the Industrial Emissions Directive, [126] which stipulates a minimum temperature of 850 °C for at least two seconds. [127]

History

The development of plastics has evolved from the use of naturally plastic materials (e.g., gums and shellac) to the use of the chemical modification of those materials (e.g., natural rubber, cellulose, collagen, and milk proteins), and finally to completely synthetic plastics (e.g., bakelite, epoxy, and PVC). Early plastics were bio-derived materials such as egg and blood proteins, which are organic polymers. In around 1600 BC, Mesoamericans used natural rubber for balls, bands, and figurines. [4] Treated cattle horns were used as windows for lanterns in the Middle Ages. Materials that mimicked the properties of horns were developed by treating milk proteins with lye. In the nineteenth century, as chemistry developed during the Industrial Revolution, many materials were reported. The development of plastics accelerated with Charles Goodyear's 1839 discovery of vulcanization to harden natural rubber.

Plaque commemorating Parkes at the Birmingham Science Museum Alexander Parkes Blue Plaque.jpg
Plaque commemorating Parkes at the Birmingham Science Museum

Parkesine, invented by Alexander Parkes in 1855 and patented the following year, [128] is considered the first man-made plastic. It was manufactured from cellulose (the major component of plant cell walls) treated with nitric acid as a solvent. The output of the process (commonly known as cellulose nitrate or pyroxilin) could be dissolved in alcohol and hardened into a transparent and elastic material that could be molded when heated. [129] By incorporating pigments into the product, it could be made to resemble ivory. Parkesine was unveiled at the 1862 International Exhibition in London and garnered for Parkes the bronze medal. [130]

In 1893, French chemist Auguste Trillat discovered the means to insolubilize casein (milk proteins) by immersion in formaldehyde, producing material marketed as galalith. [131] In 1897, mass-printing press owner Wilhelm Krische of Hanover, Germany, was commissioned to develop an alternative to blackboards. [131] The resultant horn-like plastic made from casein was developed in cooperation with the Austrian chemist (Friedrich) Adolph Spitteler (1846–1940). Although unsuitable for the intended purpose, other uses would be discovered. [131]

The world's first fully synthetic plastic was Bakelite, invented in New York in 1907 by Leo Baekeland, [5] who coined the term plastics. [6] Many chemists have contributed to the materials science of plastics, including Nobel laureate Hermann Staudinger, who has been called "the father of polymer chemistry," and Herman Mark, known as "the father of polymer physics." [7]

After World War I, improvements in chemistry led to an explosion of new forms of plastics, with mass production beginning in the 1940s and 1950s. [55] Among the earliest examples in the wave of new polymers were polystyrene (first produced by BASF in the 1930s) [4] and polyvinyl chloride (first created in 1872 but commercially produced in the late 1920s). [4] In 1923, Durite Plastics, Inc., was the first manufacturer of phenol-furfural resins. [132] In 1933, polyethylene was discovered by Imperial Chemical Industries (ICI) researchers Reginald Gibson and Eric Fawcett. [4]

The discovery of polyethylene terephthalate is credited to employees of the Calico Printers' Association in the UK in 1941; it was licensed to DuPont for the US and ICI otherwise, and as one of the few plastics appropriate as a replacement for glass in many circumstances, resulting in widespread use for bottles in Europe. [4] In 1954 polypropylene was discovered by Giulio Natta and began to be manufactured in 1957. [4] Also in 1954 expanded polystyrene (used for building insulation, packaging, and cups) was invented by Dow Chemical. [4]

Policy

Work is currently underway to develop a global treaty on plastic pollution. On March 2, 2022 UN Member States voted at the resumed fifth UN Environment Assembly (UNEA-5.2) to establish an Intergovernmental Negotiating Committee (INC) with the mandate of advancing a legally-binding international agreement on plastics. [133] The resolution is entitled "End plastic pollution: Towards an international legally binding instrument." The mandate specifies that the INC must begin its work by the end of 2022 with the goal of "completing a draft global legally binding agreement by the end of 2024." [134]

See also

Plastic in the sense of malleable

Related Research Articles

<span class="mw-page-title-main">Polyvinyl chloride</span> Common synthetic polymer

Polyvinyl chloride (alternatively: poly(vinyl chloride), colloquial: polyvinyl, or simply vinyl; abbreviated: PVC) is the world's third-most widely produced synthetic polymer of plastic (after polyethylene and polypropylene). About 40 million tons of PVC are produced each year.

<span class="mw-page-title-main">Biodegradation</span> Decomposition by living organisms

Biodegradation is the breakdown of organic matter by microorganisms, such as bacteria and fungi. It is generally assumed to be a natural process, which differentiates it from composting. Composting is a human-driven process in which biodegradation occurs under a specific set of circumstances.

<span class="mw-page-title-main">Polystyrene</span> Polymer resin widely used in packaging

Polystyrene (PS) is a synthetic polymer made from monomers of the aromatic hydrocarbon styrene. Polystyrene can be solid or foamed. General-purpose polystyrene is clear, hard, and brittle. It is an inexpensive resin per unit weight. It is a poor barrier to air and water vapor and has a relatively low melting point. Polystyrene is one of the most widely used plastics, with the scale of its production being several million tonnes per year. Polystyrene is naturally transparent, but can be colored with colorants. Uses include protective packaging, containers, lids, bottles, trays, tumblers, disposable cutlery, in the making of models, and as an alternative material for phonograph records.

<span class="mw-page-title-main">Polymer degradation</span> Alteration in the polymer properties under the influence of environmental factors

Polymer degradation is the reduction in the physical properties of a polymer, such as strength, caused by changes in its chemical composition. Polymers and particularly plastics are subject to degradation at all stages of their product life cycle, including during their initial processing, use, disposal into the environment and recycling. The rate of this degradation varies significantly; biodegradation can take decades, whereas some industrial processes can completely decompose a polymer in hours.

<span class="mw-page-title-main">Plastic recycling</span> Processes which convert waste plastic into new items

Plastic recycling is the processing of plastic waste into other products. Recycling can reduce dependence on landfill, conserve resources and protect the environment from plastic pollution and greenhouse gas emissions. Recycling rates lag those of other recoverable materials, such as aluminium, glass and paper. From the start of production through to 2015, the world produced some 6.3 billion tonnes of plastic waste, only 9% of which has been recycled, and only ~1% has been recycled more than once. Of the remaining waste, 12% was incinerated and 79% either sent to landfill or lost into the environment as pollution.

<span class="mw-page-title-main">Bioplastic</span> Plastics derived from renewable biomass sources

Bioplastics are plastic materials produced from renewable biomass sources, such as vegetable fats and oils, corn starch, straw, woodchips, sawdust, recycled food waste, etc. Some bioplastics are obtained by processing directly from natural biopolymers including polysaccharides and proteins, while others are chemically synthesised from sugar derivatives and lipids from either plants or animals, or biologically generated by fermentation of sugars or lipids. In contrast, common plastics, such as fossil-fuel plastics are derived from petroleum or natural gas.

Polyethylene or polythene film biodegrades naturally, albeit over a long period of time. Methods are available to make it more degradable under certain conditions of sunlight, moisture, oxygen, and composting and enhancement of biodegradation by reducing the hydrophobic polymer and increasing hydrophilic properties.

<span class="mw-page-title-main">Biodegradable plastic</span> Plastics that can be decomposed by the action of living organisms

Biodegradable plastics are plastics that can be decomposed by the action of living organisms, usually microbes, into water, carbon dioxide, and biomass. Biodegradable plastics are commonly produced with renewable raw materials, micro-organisms, petrochemicals, or combinations of all three.

<span class="mw-page-title-main">Plastic bottle</span> Narrow-necked container

A plastic bottle is a bottle constructed from high-density or low density plastic. Plastic bottles are typically used to store liquids such as water, soft drinks, motor oil, cooking oil, medicine, shampoo, milk, and ink. The size ranges from very small bottles to large carboys. Consumer blow molded containers often have integral handles or are shaped to facilitate grasping.

<span class="mw-page-title-main">Commodity plastics</span> Inexpensive plastics with weak mechanical properties

Commodity plastics or commodity polymers are plastics produced in high volumes for applications where exceptional material properties are not needed. In contrast to engineering plastics, commodity plastics tend to be inexpensive to produce and exhibit relatively weak mechanical properties. Some examples of commodity plastics are polyethylene, polypropylene, polystyrene, polyvinyl chloride, and poly(methyl methacrylate) .Globally, the most widely used thermoplastics include both polypropylene and polyethylene. Products made from commodity plastics include disposable plates, disposable cups, photographic and magnetic tape, clothing, reusable bags, medical trays, and seeding trays.

Polymer stabilizers are chemical additives which may be added to polymeric materials, such as plastics and rubbers, to inhibit or retard their degradation. Common polymer degradation processes include oxidation, UV-damage, thermal degradation, ozonolysis, combinations thereof such as photo-oxidation, as well as reactions with catalyst residues, dyes, or impurities. All of these degrade the polymer at a chemical level, via chain scission, uncontrolled recombination and cross-linking, which adversely affects many key properties such as strength, malleability, appearance and colour.

<span class="mw-page-title-main">Photo-oxidation of polymers</span>

In polymer chemistry photo-oxidation is the degradation of a polymer surface due to the combined action of light and oxygen. It is the most significant factor in the weathering of plastics. Photo-oxidation causes the polymer chains to break, resulting in the material becoming increasingly brittle. This leads to mechanical failure and, at an advanced stage, the formation of microplastics. In textiles the process is called phototendering.

Oxo-degradation is a process of plastic degradation utilizing oxidation to reduce the molecular weight of plastic, rendering the material accessible to bacterial and fungal decomposition. To change the Molecular structure in order to break down under sunlight, the plastic can be broken down and eaten by micro-organisms. Oxo-degradable plastics- composed of polymers such as polyethylene (PE) or polypropylene (PP) -contain a prodegradant catalyst, typically a salt of manganese or iron.

<span class="mw-page-title-main">Biodegradable bag</span> Bag capable of being decomposed

Biodegradable bags are bags that are capable of being decomposed by bacteria or other living organisms.

<span class="mw-page-title-main">Plastic pollution</span> Accumulation of plastic in natural ecosystems

Plastic pollution is the accumulation of plastic objects and particles in the Earth's environment that adversely affects humans, wildlife and their habitat. Plastics that act as pollutants are categorized by size into micro-, meso-, or macro debris. Plastics are inexpensive and durable, making them very adaptable for different uses; as a result, manufacturers choose to use plastic over other materials. However, the chemical structure of most plastics renders them resistant to many natural processes of degradation and as a result they are slow to degrade. Together, these two factors allow large volumes of plastic to enter the environment as mismanaged waste which persists in the ecosystem and travels throughout food webs.

Biodegradable additives are additives that enhance the biodegradation of polymers by allowing microorganisms to utilize the carbon within the polymer chain as a source of energy. Biodegradable additives attract microorganisms to the polymer through quorum sensing after biofilm creation on the plastic product. Additives are generally in masterbatch formation that use carrier resins such as polyethylene (PE), polypropylene (PP), polystyrene (PS) or polyethylene terephthalate (PET).

<span class="mw-page-title-main">Plastisphere</span> Plastic debris suspended in water and organisms which live in it

The plastisphere consists of ecosystems that have evolved to live in human-made plastic environments. All plastic accumulated in marine ecosystems serves as a habitat for various types of microorganisms, with the most notable contaminant being microplastics. There are an estimate of about 51 trillion microplastics floating in the oceans. Relating to the plastisphere, over 1,000 different species of microbes are able to inhabit just one of these 5mm pieces of plastic.

<span class="mw-page-title-main">Economics of plastics processing</span> Economic aspects of plastic manufacturing


The economics of plastics processing is determined by the type of process. Plastics can be processed with the following methods: machining, compression molding, transfer molding, injection molding, extrusion, rotational molding, blow molding, thermoforming, casting, forging, and foam molding. Processing methods are selected based on equipment cost, production rate, tooling cost, and build volume. High equipment and tooling cost methods are typically used for large production volumes whereas low - medium equipment cost and tooling cost methods are used for low production volumes. Compression molding, transfer molding, injection molding, forging, and foam molding have high equipment and tooling cost. Lower cost processes are machining, extruding, rotational molding, blow molding, thermoforming, and casting. A summary of each process and its cost is displayed in figure 1.

<span class="mw-page-title-main">Polymateria</span> British private technology company

Polymateria Ltd is a British technology company developing biodegradable plastic alternatives. In 2020, the privately owned company was the first to achieve certified biodegradation of the most commonly-littered forms of plastic packaging in real-world conditions, in less than a year without creating microplastics.

<span class="mw-page-title-main">Plastic degradation by marine bacteria</span> Ability of bacteria to break down plastic polymers

Plastic degradation in marine bacteria describes when certain pelagic bacteria break down polymers and use them as a primary source of carbon for energy. Polymers such as polyethylene (PE), polypropylene (PP), and polyethylene terephthalate (PET) are incredibly useful for their durability and relatively low cost of production, however it is their persistence and difficulty to be properly disposed of that is leading to pollution of the environment and disruption of natural processes. It is estimated that each year there are 9-14 million metric tons of plastic that are entering the ocean due to inefficient solutions for their disposal. The biochemical pathways that allow for certain microbes to break down these polymers into less harmful byproducts has been a topic of study to develop a suitable anti-pollutant.

References

  1. "Life Cycle of a Plastic Product". Americanchemistry.com. Archived from the original on March 17, 2010. Retrieved July 1, 2011.
  2. 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 Environment, U. N. (October 21, 2021). "Drowning in Plastics – Marine Litter and Plastic Waste Vital Graphics". UNEP - UN Environment Programme. Retrieved March 21, 2022.
  3. "The environmental impacts of plastics and micro-plastics use, waste and pollution: EU and national measures" (PDF). europarl.europa.eu. October 2020.
  4. 1 2 3 4 5 6 7 8 9 10 11 Andrady AL, Neal MA (July 2009). "Applications and societal benefits of plastics". Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences. 364 (1526): 1977–84. doi:10.1098/rstb.2008.0304. PMC   2873019 . PMID   19528050.
  5. 1 2 American Chemical Society National Historic Chemical Landmarks. "Bakelite: The World's First Synthetic Plastic" . Retrieved February 23, 2015.
  6. 1 2 Edgar D, Edgar R (2009). Fantastic Recycled Plastic: 30 Clever Creations to Spark Your Imagination. Sterling Publishing Company, Inc. ISBN   978-1-60059-342-0 via Google Books.
  7. 1 2 Teegarden DM (2004). Polymer Chemistry: Introduction to an Indispensable Science. NSTA Press. ISBN   978-0-87355-221-9 via Google Books.
  8. "Plastikos" πλαστι^κ-ός. Henry George Liddell, Robert Scott, A Greek-English Lexicon. Retrieved July 1, 2011.
  9. "Plastic". Online Etymology Dictionary. Retrieved July 29, 2021.
  10. Ebbing D, Gammon SD (2016). General Chemistry. Cengage Learning. ISBN   978-1-305-88729-9.
  11. "Classification of Plastics". Joanne and Steffanie's Plastics Web Site. Archived from the original on December 15, 2007. Retrieved July 1, 2011.
  12. Kent R. "Periodic Table of Polymers". Plastics Consultancy Network. Archived from the original on July 3, 2008.
  13. "Composition and Types of Plastic". Infoplease. Archived from the original on October 15, 2012. Retrieved September 29, 2009.
  14. Gilleo K (2004). Area Array Packaging Processes: For BGA, Flip Chip, and CSP. McGraw Hill Professional. ISBN   978-0-07-142829-3 via Google Books.
  15. Kutz M (2002). Handbook of Materials Selection. John Wiley & Sons. ISBN   978-0-471-35924-1 via Google Books.
  16. Heeger AJ, Kivelson S, Schrieffer JR, Su WP (1988). "Solitons in Conducting Polymers". Reviews of Modern Physics. 60 (3): 781–850. Bibcode:1988RvMP...60..781H. doi:10.1103/RevModPhys.60.781.
  17. "Properties of Copper". Copper Development Association.
  18. Brandl H, Püchner P (1992). "Biodegradation Biodegradation of Plastic Bottles Made from 'Biopol' in an Aquatic Ecosystem Under In Situ Conditions". Biodegradation. 2 (4): 237–43. doi:10.1007/BF00114555. S2CID   37486324.
  19. "Biochemical Opportunities in the UK, NNFCC 08-008 — NNFCC". Archived from the original on July 20, 2011. Retrieved March 24, 2011.
  20. "Bioplastics industry shows dynamic growth". December 5, 2019.
  21. "Becoming Employed in a Growing Bioplastics Industry - bioplastics MAGAZINE". www.bioplasticsmagazine.com.
  22. Galie F (November 2016). "Global Market Trends and Investments in Polyethylene and Polyproplyene" (PDF). ICIS Whitepaper. Reed business Information, Inc. Retrieved December 16, 2017.
  23. 1 2 3 4 5 Geyer, Roland; Jambeck, Jenna R.; Law, Kara Lavender (July 2017). "Production, use, and fate of all plastics ever made". Science Advances. 3 (7): e1700782. Bibcode:2017SciA....3E0782G. doi: 10.1126/sciadv.1700782 . PMC   5517107 . PMID   28776036.
  24. "Top 100 Producers: The Minderoo Foundation". www.minderoo.org. Retrieved October 14, 2021.
  25. 1 2 "Plastics – the Facts 2020" (PDF). Archived from the original (PDF) on October 7, 2021.
  26. 1 2 PP&A stand for polyester, polyamide and acrylate polymers; all of which are used to make synthetic fibres. Care should be taken not to confuse it with polyphthalamide (PPA)
  27. The majority of polyurethanes are thermosets, however some thermoplastics are also produced, for instance spandex
  28. "Plastic Recycling Factsheet" (PDF). EuRIC - European Recycling Industries’ Confederation. Retrieved November 9, 2021.
  29. "Polymers in aerospace applications". Euroshore. Retrieved June 2, 2021.
  30. "Sustainable packaging materials for snacks". October 28, 2021. Archived from the original on October 28, 2021. Retrieved September 10, 2022.
  31. 1 2 3 Hahladakis JN, Velis CA, Weber R, Iacovidou E, Purnell P (February 2018). "An overview of chemical additives present in plastics: Migration, release, fate and environmental impact during their use, disposal and recycling". Journal of Hazardous Materials. 344: 179–199. doi: 10.1016/j.jhazmat.2017.10.014 . PMID   29035713.
  32. Marturano, Valentina; Cerruti, Pierfrancesco; Ambrogi, Veronica (June 27, 2017). "Polymer additives". Physical Sciences Reviews. 2 (6): 130. Bibcode:2017PhSRv...2..130M. doi: 10.1515/psr-2016-0130 . S2CID   199059895.
  33. Pfaendner, Rudolf (September 2006). "How will additives shape the future of plastics?". Polymer Degradation and Stability. 91 (9): 2249–2256. doi:10.1016/j.polymdegradstab.2005.10.017.
  34. "Mapping exercise – Plastic additives initiative - ECHA". echa.europa.eu. Retrieved May 3, 2022.
  35. Wiesinger, Helene; Wang, Zhanyun; Hellweg, Stefanie (July 6, 2021). "Deep Dive into Plastic Monomers, Additives, and Processing Aids". Environmental Science & Technology . 55 (13): 9339–9351. Bibcode:2021EnST...55.9339W. doi:10.1021/acs.est.1c00976. hdl: 20.500.11850/495854 . PMID   34154322. S2CID   235597312.
  36. "Emission Scenario Documents: N°3 Plastic Additives (2004, revised in 2009)". Organisation for Economic Co-operation and Development. Retrieved May 19, 2022.
  37. Elias, Hans-Georg; Mülhaupt, Rolf (April 14, 2015). "Plastics, General Survey, 1. Definition, Molecular Structure and Properties". Ullmann's Encyclopedia of Industrial Chemistry: 1–70. doi:10.1002/14356007.a20_543.pub2. ISBN   9783527306732.
  38. 1 2 Teuten EL, Saquing JM, Knappe DR, Barlaz MA, Jonsson S, Björn A, et al. (July 2009). "Transport and release of chemicals from plastics to the environment and to wildlife". Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences. 364 (1526): 2027–45. doi:10.1098/rstb.2008.0284. PMC   2873017 . PMID   19528054.
  39. "New disease caused by plastics discovered in seabirds". The Guardian. March 3, 2023. Retrieved March 4, 2023.
  40. "New disease caused solely by plastics discovered in seabirds". Natural History Museum. March 3, 2023. Retrieved March 4, 2023.
  41. "Impact modifiers: how to make your compound tougher". Plastics, Additives and Compounding. 6 (3): 46–49. May 2004. doi:10.1016/S1464-391X(04)00203-X.
  42. Hahladakis JN, Velis CA, Weber R, Iacovidou E, Purnell P (February 2018). "An overview of chemical additives present in plastics: Migration, release, fate and environmental impact during their use, disposal and recycling". Journal of Hazardous Materials. 344: 179–199. doi: 10.1016/j.jhazmat.2017.10.014 . PMID   29035713. Open Access logo PLoS transparent.svg
  43. 1 2 3 McRandle PW (March–April 2004). "Plastic Water Bottles". National Geographic . Retrieved November 13, 2007.
  44. Yang CZ, Yaniger SI, Jordan VC, Klein DJ, Bittner GD (July 2011). "Most plastic products release estrogenic chemicals: a potential health problem that can be solved". Environmental Health Perspectives. 119 (7): 989–96. doi:10.1289/ehp.1003220. PMC   3222987 . PMID   21367689.
  45. Rubin BS, Murray MK, Damassa DA, King JC, Soto AM (July 2001). "Perinatal exposure to low doses of bisphenol A affects body weight, patterns of estrous cyclicity, and plasma LH levels". Environmental Health Perspectives. 109 (7): 675–80. doi:10.2307/3454783. JSTOR   3454783. PMC   1240370 . PMID   11485865.
  46. Alonso-Magdalena P, Morimoto S, Ripoll C, Fuentes E, Nadal A (January 2006). "The estrogenic effect of bisphenol A disrupts pancreatic beta-cell function in vivo and induces insulin resistance". Environmental Health Perspectives. 114 (1): 106–12. doi:10.1289/ehp.8451. PMC   1332664 . PMID   16393666. Archived from the original on January 19, 2009.
  47. Zajac A (January 16, 2010). "FDA Issues BPA Guidelines". Los Angeles Times. Retrieved July 29, 2021.
  48. McCormick LW (October 30, 2009). "More Kids' Products Found Containing Unsafe Chemicals". ConsumerAffairs.com.
  49. Weisman A (2007). The world without us. New York: Thomas Dunne Books/St. Martin's Press. ISBN   978-1-4434-0008-4.
  50. Geyer R, Jambeck JR, Law KL (July 2017). "Production, use, and fate of all plastics ever made". Science Advances. 3 (7): e1700782. Bibcode:2017SciA....3E0782G. doi:10.1126/sciadv.1700782. PMC   5517107 . PMID   28776036.
  51. Leung H (April 21, 2018). "Five Asian Countries Dump More Plastic Into Oceans Than Anyone Else Combined: How You Can Help". Forbes . Retrieved June 23, 2019. China, Indonesia, Philippines, Thailand, and Vietnam are dumping more plastic into oceans than the rest of the world combined, according to a 2017 report by Ocean Conservancy
  52. Schmidt C, Krauth T, Wagner S (November 2017). "Export of Plastic Debris by Rivers into the Sea" (PDF). Environmental Science & Technology. 51 (21): 12246–12253. Bibcode:2017EnST...5112246S. doi:10.1021/acs.est.7b02368. PMID   29019247. The 10 top-ranked rivers transport 88–95% of the global load into the sea
  53. Franzen H (November 30, 2017). "Almost all plastic in the ocean comes from just 10 rivers". Deutsche Welle . Retrieved December 18, 2018. It turns out that about 90 percent of all the plastic that reaches the world's oceans gets flushed through just 10 rivers: The Yangtze, the Indus, Yellow River, Hai River, the Nile, the Ganges, Pearl River, Amur River, the Niger, and the Mekong (in that order).
  54. 1 2 3 4 Barnes DK, Galgani F, Thompson RC, Barlaz M (July 2009). "Accumulation and fragmentation of plastic debris in global environments". Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences. 364 (1526): 1985–98. doi:10.1098/rstb.2008.0205. PMC   2873009 . PMID   19528051.
  55. 1 2 Thompson RC, Swan SH, Moore CJ, vom Saal FS (July 2009). "Our plastic age". Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences. 364 (1526): 1973–6. doi:10.1098/rstb.2009.0054. PMC   2874019 . PMID   19528049.
  56. Carrington, Damian (December 7, 2021). "'Disastrous' plastic use in farming threatens food safety – UN". The Guardian. Retrieved December 8, 2021.
  57. Cabernard, Livia; Pfister, Stephan; Oberschelp, Christopher; Hellweg, Stefanie (December 2, 2021). "Growing environmental footprint of plastics driven by coal combustion". Nature Sustainability. 5 (2): 139–148. Bibcode:2021NatSu...5..139C. doi: 10.1038/s41893-021-00807-2 . hdl: 20.500.11850/518642 . ISSN   2398-9629. S2CID   244803448.
  58. 1 2 3 Ghosh, Shampa; Sinha, Jitendra Kumar; Ghosh, Soumya; Vashisth, Kshitij; Han, Sungsoo; Bhaskar, Rakesh (January 2023). "Microplastics as an Emerging Threat to the Global Environment and Human Health". Sustainability. 15 (14): 10821. doi: 10.3390/su151410821 . ISSN   2071-1050.
  59. Arthur, Courtney; Baker, Joel; Bamford, Holly (2009). "Proceedings of the International Research Workshop on the Occurrence, Effects and Fate of Microplastic Marine Debris" (PDF). NOAA Technical Memorandum. Archived (PDF) from the original on April 28, 2021. Retrieved October 25, 2018.
  60. Collignon, Amandine; Hecq, Jean-Henri; Galgani, François; Collard, France; Goffart, Anne (2014). "Annual variation in neustonic micro- and meso-plastic particles and zooplankton in the Bay of Calvi (Mediterranean–Corsica)" (PDF). Marine Pollution Bulletin. 79 (1–2): 293–298. Bibcode:2014MarPB..79..293C. doi:10.1016/j.marpolbul.2013.11.023. PMID   24360334. Archived (PDF) from the original on September 20, 2021. Retrieved February 6, 2019.
  61. European Chemicals Agency. "Restricting the use of intentionally added microplastic particles to consumer or professional use products of any kind". ECHA. European Commission. Archived from the original on January 15, 2022. Retrieved September 8, 2020.
  62. 1 2 3 4 Ghosh, Shampa; Sinha, Jitendra Kumar; Ghosh, Soumya; Vashisth, Kshitij; Han, Sungsoo; Bhaskar, Rakesh (June 2023). "Microplastics as an Emerging Threat to the Global Environment and Human Health". Sustainability. 15 (14): 10821. doi: 10.3390/su151410821 . ISSN   2071-1050.
  63. Green, DS; Jefferson, M; Boots, B; Stone, L (January 2021). "All that glitters is litter? Ecological impacts of conventional versus biodegradable glitter in a freshwater habitat". Journal of Hazardous Materials. 402: 124070. doi:10.1016/j.jhazmat.2020.124070. ISSN   0304-3894. PMID   33254837. S2CID   224894411.
  64. Cole, M; Lindeque, P; Fileman, E; Halsband, C; Goodhead, R; Moger, J; Galloway, TS (2013). "Microplastic Ingestion by Zooplankton". Environmental Science & Technology. 47 (12): 6646–55. Bibcode:2013EnST...47.6646C. doi:10.1021/es400663f. hdl: 10871/19651 . PMID   23692270.
  65. "Where Does Marine Litter Come From?". Marine Litter Facts. British Plastics Federation. Archived from the original on May 18, 2021. Retrieved September 25, 2018.
  66. 1 2 Boucher, Julien; Friot, Damien (2017). Primary microplastics in the oceans: A global evaluation of sources. doi:10.2305/IUCN.CH.2017.01.en. ISBN   978-2831718279.
  67. Kovochich, M; Liong, M; Parker, JA; Oh, SC; Lee, JP; Xi, L; Kreider, ML; Unice, KM (February 2021). "Chemical mapping of tire and road wear particles for single particle analysis". Science of the Total Environment. 757: 144085. Bibcode:2021ScTEn.757n4085K. doi: 10.1016/j.scitotenv.2020.144085 . ISSN   0048-9697. PMID   33333431. S2CID   229318535.
  68. Conkle, JL; Báez Del Valle, CD; Turner, JW (2018). "Are We Underestimating Microplastic Contamination in Aquatic Environments?". Environmental Management. 61 (1): 1–8. Bibcode:2018EnMan..61....1C. doi:10.1007/s00267-017-0947-8. PMID   29043380. S2CID   40970384.
  69. "Plastic free July: How to stop accidentally consuming plastic particles from packaging". Stuff. July 11, 2019. Archived from the original on November 4, 2021. Retrieved April 13, 2021.
  70. "Development solutions: Building a better ocean". European Investment Bank. Archived from the original on October 21, 2021. Retrieved August 19, 2020.
  71. Resnick, Brian (September 19, 2018). "More than ever, our clothes are made of plastic. Just washing them can pollute the oceans". Vox. Archived from the original on January 5, 2022. Retrieved October 4, 2021.
  72. Chamas, Ali; Moon, Hyunjin; Zheng, Jiajia; Qiu, Yang; Tabassum, Tarnuma; Jang, Jun Hee; Abu-Omar, Mahdi; Scott, Susannah L.; Suh, Sangwon (2020). "Degradation Rates of Plastics in the Environment". ACS Sustainable Chemistry & Engineering. 8 (9): 3494–3511. doi: 10.1021/acssuschemeng.9b06635 .
  73. Klein S, Dimzon IK, Eubeler J, Knepper TP (2018). "Analysis, Occurrence, and Degradation of Microplastics in the Aqueous Environment". In Wagner M, Lambert S (eds.). Freshwater Microplastics. The Handbook of Environmental Chemistry. Vol. 58. Cham.: Springer. pp. 51–67. doi:10.1007/978-3-319-61615-5_3. ISBN   978-3319616148. See Section 3, "Environmental Degradation of Synthetic Polymers".
  74. Grossman, Elizabeth (January 15, 2015). "How Plastics from Your Clothes Can End up in Your Fish". Time. Archived from the original on November 18, 2020. Retrieved March 15, 2015.
  75. "How Long Does it Take Trash to Decompose". 4Ocean. January 20, 2017. Archived from the original on September 25, 2018. Retrieved September 25, 2018.
  76. "Why food's plastic problem is bigger than we realise". www.bbc.com. Archived from the original on November 18, 2021. Retrieved March 27, 2021.
  77. Nex, Sally (2021). How to garden the low carbon way: the steps you can take to help combat climate change (First American ed.). New York. ISBN   978-0744029284. OCLC   1241100709.{{cite book}}: CS1 maint: location missing publisher (link)
  78. Xue B, Zhang L, Li R, Wang Y, Guo J, Yu K, Wang S (February 2020). "Underestimated Microplastic Pollution Derived from Fishery Activities and "Hidden" in Deep Sediment". Environmental Science & Technology. 54 (4): 2210–2217. Bibcode:2020EnST...54.2210X. doi:10.1021/acs.est.9b04850. PMID   31994391. S2CID   210950462.
  79. "No mountain high enough: study finds plastic in 'clean' air". The Guardian. AFP. December 21, 2021. Archived from the original on January 14, 2022. Retrieved December 21, 2021.
  80. Blackburn K, Green D (March 2022). "The potential effects of microplastics on human health: What is known and what is unknown". Ambio (Review). 51 (3): 518–530. Bibcode:2022Ambio..51..518B. doi:10.1007/s13280-021-01589-9. PMC   8800959 . PMID   34185251.
  81. American Chemical Society. "Plastics In Oceans Decompose, Release Hazardous Chemicals, Surprising New Study Says". Science Daily. Retrieved March 15, 2015.
  82. Le Guern C (March 2018). "When The Mermaids Cry: The Great Plastic Tide". Coastal Care. Archived from the original on April 5, 2018. Retrieved November 10, 2018.
  83. Kinoshita S, Kageyama S, Iba K, Yamada Y, Okada H (1975). "Utilization of a Cyclic Dimer and Linear Oligomers of E-Aminocaproic Acid by Achromobacter Guttatus". Agricultural and Biological Chemistry. 39 (6): 1219–1223. doi: 10.1271/bbb1961.39.1219 .
  84. 1 2 Tokiwa Y, Calabia BP, Ugwu CU, Aiba S (August 2009). "Biodegradability of plastics". International Journal of Molecular Sciences. 10 (9): 3722–42. doi: 10.3390/ijms10093722 . PMC   2769161 . PMID   19865515.
  85. Russell JR, Huang J, Anand P, Kucera K, Sandoval AG, Dantzler KW, et al. (September 2011). "Biodegradation of polyester polyurethane by endophytic fungi". Applied and Environmental Microbiology. 77 (17): 6076–84. Bibcode:2011ApEnM..77.6076R. doi:10.1128/aem.00521-11. PMC   3165411 . PMID   21764951.
  86. Russell JR, Huang J, Anand P, Kucera K, Sandoval AG, Dantzler KW, et al. (September 2011). "Biodegradation of polyester polyurethane by endophytic fungi". Applied and Environmental Microbiology. 77 (17): 6076–84. Bibcode:2011ApEnM..77.6076R. doi:10.1128/AEM.00521-11. PMC   3165411 . PMID   21764951.
  87. "Deep Geologic Repository Project" (PDF). Ceaa-acee.gc.ca. Retrieved April 18, 2017.
  88. Roy R (March 7, 2006). "Immortal Polystyrene Foam Meets its Enemy". Livescience.com. Retrieved April 18, 2017.
  89. Ward PG, Goff M, Donner M, Kaminsky W, O'Connor KE (April 2006). "A two step chemo-biotechnological conversion of polystyrene to a biodegradable thermoplastic". Environmental Science & Technology. 40 (7): 2433–7. Bibcode:2006EnST...40.2433W. doi:10.1021/es0517668. PMID   16649270.
  90. Cacciari I, Quatrini P, Zirletta G, Mincione E, Vinciguerra V, Lupattelli P, Giovannozzi Sermanni G (November 1993). "Isotactic polypropylene biodegradation by a microbial community: physicochemical characterization of metabolites produced". Applied and Environmental Microbiology. 59 (11): 3695–700. Bibcode:1993ApEnM..59.3695C. doi: 10.1128/AEM.59.11.3695-3700.1993 . PMC   182519 . PMID   8285678.
  91. 1 2 3 Ishtiaq AM (2011). Microbial Degradation of Polyvinyl Chloride Plastics (PDF) (Ph.D.). Islamabad: Quaid-i-Azam University. Archived from the original (PDF) on December 24, 2013. Retrieved December 23, 2013.
  92. Gusse AC, Miller PD, Volk TJ (July 2006). "White-rot fungi demonstrate first biodegradation of phenolic resin". Environmental Science & Technology. 40 (13): 4196–9. Bibcode:2006EnST...40.4196G. doi:10.1021/es060408h. PMID   16856735.
  93. "CanadaWorld – WCI student isolates microbe that lunches on plastic bags". The Record.com. Archived from the original on July 18, 2011.
  94. Hadad D, Geresh S, Sivan A (2005). "Biodegradation of polyethylene by the thermophilic bacterium Brevibacillus borstelensis". Journal of Applied Microbiology. 98 (5): 1093–100. doi:10.1111/j.1365-2672.2005.02553.x. PMID   15836478. S2CID   2977246.
  95. Bell TE (2007). "Preventing "Sick" Spaceships".
  96. Cappitelli F, Sorlini C (February 2008). "Microorganisms attack synthetic polymers in items representing our cultural heritage". Applied and Environmental Microbiology. 74 (3): 564–9. Bibcode:2008ApEnM..74..564C. doi:10.1128/AEM.01768-07. PMC   2227722 . PMID   18065627.
  97. Zaikab GD (March 2011). "Marine Microbes Digest Plastic". Nature. doi: 10.1038/news.2011.191 .
  98. Sharon, Chetna; Sharon, Madhuri (2012). "Studies on Biodegradation of Polyethylene terephthalate: A synthetic polymer". Journal of Microbiology and Biotechnology Research. 2 (2) via ResearchGate.
  99. Bosch X (2001). "Fungus Eats CD". Nature. doi:10.1038/news010628-11.
  100. "Fungus 'Eats' CDs". BBC News. June 22, 2001.
  101. Cappitelli F, Principi P, Sorlini C (August 2006). "Biodeterioration of modern materials in contemporary collections: can biotechnology help?". Trends in Biotechnology. 24 (8): 350–4. doi:10.1016/j.tibtech.2006.06.001. PMID   16782219.
  102. Rinaldi A (November 2006). "Saving a fragile legacy. Biotechnology and microbiology are increasingly used to preserve and restore the world's cultural heritage". EMBO Reports. 7 (11): 1075–9. doi:10.1038/sj.embor.7400844. PMC   1679785 . PMID   17077862.
  103. Al-Salem, S.M.; Lettieri, P.; Baeyens, J. (October 2009). "Recycling and recovery routes of plastic solid waste (PSW): A review". Waste Management. 29 (10): 2625–2643. Bibcode:2009WaMan..29.2625A. doi:10.1016/j.wasman.2009.06.004. PMID   19577459.
  104. Ignatyev, I.A.; Thielemans, W.; Beke, B. Vander (2014). "Recycling of Polymers: A Review". ChemSusChem . 7 (6): 1579–1593. doi:10.1002/cssc.201300898. PMID   24811748.
  105. Lazarevic, David; Aoustin, Emmanuelle; Buclet, Nicolas; Brandt, Nils (December 2010). "Plastic waste management in the context of a European recycling society: Comparing results and uncertainties in a life cycle perspective". Resources, Conservation and Recycling. 55 (2): 246–259. doi:10.1016/j.resconrec.2010.09.014.
  106. Hopewell, Jefferson; Dvorak, Robert; Kosior, Edward (July 27, 2009). "Plastics recycling: challenges and opportunities". Philosophical Transactions of the Royal Society B: Biological Sciences. 364 (1526): 2115–2126. doi:10.1098/rstb.2008.0311. PMC   2873020 . PMID   19528059.
  107. Lange, Jean-Paul (November 12, 2021). "Managing Plastic Waste─Sorting, Recycling, Disposal, and Product Redesign". ACS Sustainable Chemistry & Engineering. 9 (47): 15722–15738. doi: 10.1021/acssuschemeng.1c05013 .
  108. 1 2 Geyer, Roland; Jambeck, Jenna R.; Law, Kara Lavender (July 2017). "Production, use, and fate of all plastics ever made". Science Advances. 3 (7): e1700782. Bibcode:2017SciA....3E0782G. doi: 10.1126/sciadv.1700782 . PMC   5517107 . PMID   28776036.
  109. Andrady, Anthony L. (February 1994). "Assessment of Environmental Biodegradation of Synthetic Polymers". Journal of Macromolecular Science, Part C: Polymer Reviews. 34 (1): 25–76. doi:10.1080/15321799408009632.
  110. Ahmed, Temoor; Shahid, Muhammad; Azeem, Farrukh; Rasul, Ijaz; Shah, Asad Ali; Noman, Muhammad; Hameed, Amir; Manzoor, Natasha; Manzoor, Irfan; Muhammad, Sher (March 2018). "Biodegradation of plastics: current scenario and future prospects for environmental safety". Environmental Science and Pollution Research. 25 (8): 7287–7298. doi:10.1007/s11356-018-1234-9. PMID   29332271. S2CID   3962436.
  111. Jambeck, Jenna, Science 13 February 2015: Vol. 347 no. 6223; et al. (2015). "Plastic waste inputs from land into the ocean". Science. 347 (6223): 768–771. Bibcode:2015Sci...347..768J. doi:10.1126/science.1260352. PMID   25678662. S2CID   206562155.{{cite journal}}: CS1 maint: numeric names: authors list (link)
  112. Paul, Andrew (May 8, 2023). "Recycling plants spew a staggering amount of microplastics". Popular Science. Retrieved May 8, 2023.
  113. Brown, Erina; MacDonald, Anna; Allen, Steve; Allen, Deonie (May 1, 2023). "The potential for a plastic recycling facility to release microplastic pollution and possible filtration remediation effectiveness". Journal of Hazardous Materials Advances. 10: 100309. doi: 10.1016/j.hazadv.2023.100309 . ISSN   2772-4166. S2CID   258457895.
  114. Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions – A European Strategy for Plastics in a Circular Economy, COM(2018) 28 final, 6 January 2018
  115. Huffman, George L.; Keller, Daniel J. (1973). "The Plastics Issue". Polymers and Ecological Problems. pp. 155–167. doi:10.1007/978-1-4684-0871-3_10. ISBN   978-1-4684-0873-7.
  116. National Public Radio, 12 September 2020 "How Big Oil Misled The Public Into Believing Plastic Would Be Recycled"
  117. PBS, Frontline, 31 March 2020, "Plastics Industry Insiders Reveal the Truth About Recycling"
  118. Dharna Noor (February 15, 2024). "'They lied': plastics producers deceived public about recycling, report reveals". theguardian.com. Retrieved February 16, 2024.
  119. Tullo, Alexander (October 10, 2022). "Amid controversy, industry goes all in on plastics pyrolysis". Chemical & Engineering News . Retrieved January 17, 2023.
  120. Narayanan S (December 12, 2005). "The Zadgaonkars turn carry-bags into petrol!". The Hindu. Archived from the original on November 9, 2012. Retrieved July 1, 2011.
  121. "Plastic leakage and greenhouse gas emissions are increasing". OECD. Retrieved August 11, 2022.
  122. "How is plastic made? Climate change is a key ingredient | Friends of the Earth". friendsoftheearth.uk. Retrieved February 16, 2024.
  123. De Decker K (June 2009). Grosjean V (ed.). "The monster footprint of digital technology". Low-Tech Magazine. Retrieved April 18, 2017.
  124. "How much energy does it take (on average) to produce 1 kilogram of the following materials?". Low-Tech Magazine. December 26, 2014. Retrieved April 18, 2017.
  125. Halden RU (2010). "Plastics and health risks". Annual Review of Public Health. 31: 179–94. doi: 10.1146/annurev.publhealth.012809.103714 . PMID   20070188.
  126. Romero, Lina M.; Lyczko, Nathalie; Nzihou, Ange; Antonini, Gérard; Moreau, Eric; Richardeau, Hubert; Coste, Christophe; Madoui, Saïd; Durécu, Sylvain (July 2020). "New insights on mercury abatement and modeling in a full-scale municipal solid waste incineration flue gas treatment unit". Waste Management. 113: 270–279. Bibcode:2020WaMan.113..270R. doi: 10.1016/j.wasman.2020.06.003 . PMID   32559697. S2CID   219948357.
  127. Janhäll, Sara; Petersson, Mikaela; Davidsson, Kent; Öman, Tommy; Sommertune, Jens; Kåredal, Monica; Messing, Maria E.; Rissler, Jenny (October 2021). "Release of carbon nanotubes during combustion of polymer nanocomposites in a pilot-scale facility for waste incineration". NanoImpact. 24: 100357. doi: 10.1016/j.impact.2021.100357 . PMID   35559816. S2CID   239252029.
  128. UK Patent office (1857). Patents for inventions. UK Patent office. p. 255.
  129. "Dictionary – Definition of celluloid". Websters-online-dictionary.org. Archived from the original on December 11, 2009. Retrieved October 26, 2011.
  130. Fenichell S (1996). Plastic : the making of a synthetic century . New York: HarperBusiness. p.  17. ISBN   978-0-88730-732-4.
  131. 1 2 3 Trimborn C (August 2004). "Jewelry Stone Make of Milk". GZ Art+Design. Retrieved May 17, 2010.
  132. "Historical Overview and Industrial Development". International Furan Chemicals, Inc. Retrieved May 4, 2014.
  133. Geddie, John; Brock, Joe (March 2, 2022). "'Biggest green deal since Paris': UN agrees plastic treaty roadmap". Reuters. Retrieved August 3, 2022.
  134. "Historic day in the campaign to beat plastic pollution: Nations commit to develop a legally binding agreement". UN Environment. March 2, 2022. Retrieved August 3, 2022.

Sources

Definition of Free Cultural Works logo notext.svg  This article incorporates text from a free content work. Licensed under Cc BY-SA 3.0 IGO( license statement/permission ). Text taken from Drowning in Plastics – Marine Litter and Plastic Waste Vital Graphics , United Nations Environment Programme.