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Currently, an authoritative definition of sustainable food packaging is missing, leading to a lot of confusion.
Ideally, sustainable foodware and food packaging enable circular and fair business models that deliver nutritious, safe, and culturally appropriate foodstuffs to people. They should also avoid adverse impacts that destabilize the planet's ecosystems in the long term across their entire life cycle.
In reality, many stakeholders in the food industry focus on greenhouse gas (GHG) emissions to evaluate sustainability (often communicated as CO2 emissions). Comparing such a metric only offers a one-dimensional view of sustainability and hinders capturing the known impacts of other crucial factors.
To evaluate the sustainability of foodware and food packaging holistically, the UP Scorecard adopts a multi-indicator, metrics-based approach.
The UP Scorecard uses "traditional" life cycle assessment () metrics, including , , and to evaluate impacts on the planet's ecosystems in the long term. Importantly, the UP Scorecard considers the entire life cycle of a product to paint a more realistic picture of true sustainability.
It uses the and metrics to assess the principles of the .
Finally, the UP Scorecard uses the metric to consider chemical safety in order to protect human and environmental health.
It is also important to understand that the sustainability of foodware and packaging is not solely related to the nature of the used within a foodware or packaging product. It is equally important to evaluate different and their impacts.
Plastics are lightweight, versatile, and cost-effective materials predominantly made from fossil carbon, though renewable sources are becoming more common. Since the 1950s, plastics have been widely used in food packaging, such as bottles, cups, trays, and bags.
Conventional plastics are made from fossil fuels, and their production contributes to climate change and air pollution. Certain plastics can be produced with a fraction of recycled material. However, to compensate for the degradation of polymer chains and subsequent loss of mechanical properties after use and recycling, the addition of virgin material is generally required.
If you want to learn more about plastics, you can explore the external resources linked below.
The UP Scorecard evaluates the impacts of primary food packaging, i.e. packaging in direct contact with food and beverage. Secondary packaging used to transport multiple units of a food product (such as large cardboard boxes or pallets) is not evaluated within the UP Scorecard.
Foodware and food packaging play a crucial role in our society, facilitating the storage, transportation, and preservation of foods. Food packaging materials range from plastics, paper, and glass to metals and composites. The life cycle of packaging products, from raw material extraction and manufacturing to transportation and disposal, involves energy- and resource-intensive processes and generates large amounts of waste. This results in long-term damage to humans and our planet, with impacts on climate change, ecosystem degradation, and human health. The presence of harmful chemicals of concern in foodware and packaging can further directly expose consumers and the environment, leading to harmful health impacts.
At the end of its life, food packaging will either be recovered (reused, recycled, composted) or end up as waste (incineration, landfill, or littering). Although recycling is presented as the ultimate solution to our environmental issues, it is in reality only a small part of the solution. Recycling - especially plastics recycling - will not be able to address the ever-increasing amount of single-use products.
The global production of packaging materials - including food packaging - will continue to grow exponentially, driven by the expansion of global markets. Without a significant change in our consumption habits, and a shift towards more sustainable food packaging materials systems, their contribution to exceeding planet boundaries will continue to grow.
The diverse health impacts that can be caused by food contact chemicals (FCCs), is currently underestimated and poorly assessed. As a result, regulatory bodies are basing current regulations on outdated or limited science, meaning that public health is not being properly protected.
Transitioning to more sustainable foodware and food packaging is therefore crucial for mitigating these impacts.
The term "bioplastics" has been often used interchangeably with the terms "biodegradable plastics" and "biobased plastics". This has led to some confusion among manufacturers, brand owners, and consumers alike. The graphic below provides clarity about the correct use of these terms and some of the plastic resin types that fall within each:
When bioplastics are made from renewable sources like corn or sugarcane, their production reduces reliance on fossil fuels, which reduces greenhouse gas emissions. However, their production often requires significant water, land, and chemical inputs (contributing to eutrophication and acidification), and may compete with food resources.
The chemical safety of bioplastics raises concerns. Like conventional plastics, they are chemically complex materials that can contain many different harmful chemicals, both intentionally added and non-intentionally added substances (NIAS), that can migrate into food or persist in the environment, posing risks to human health and ecosystems. Studies show that bioplastics can be as toxic or even more toxic than conventional fossil-based plastics.
The presence of potentially harmful chemicals in bioplastics also raises concerns for achieving a safe circular economy as harmful chemicals can contaminate compost, which will be released into agricultural soils when the compost is used on them.
Not all bioplastics are biodegradable, and those that are may only degrade under specific conditions that are often not met in natural environments (and instead require industrial composting facilities). This can lead to misconceptions about their environmental benefits, as products labeled as "biodegradable" might in reality not fully biodegrade and instead contribute to plastic pollution.
At the end of their life, bioplastics can also face challenges in waste management. If not properly processed separately from conventional plastics, they can disrupt recycling efforts.
When biodegradable plastics are intended for single-use applications, their degradation often results in the loss of resources and contributes to carbon emissions, offering limited environmental benefits.
If you want to learn more about bioplastics, explore the resources linked below.
Besides contributing to climate change, plastics can pollute the natural environment. When leakage happens at different life cycle stages, plastics end up in the environment (see ). Since plastics are durable materials, they remain in the environment for decades (or centuries), releasing chemicals and degrading into smaller microplastics.
Plastics are chemically complex materials. They are made of polymers and oligomers, often include various additives that enhance their properties, and contain many non-intentionally added substances () such as impurities from manufacturing, use, and recycling. These chemicals can transfer into food, a process known as , which can pose health risks for consumers. Additionally, plastics can release during their lifecycle, leading to both environmental and potential human health concerns.
The end-of-life of plastic food packaging is challenging. While is one approach to reducing environmental impact, it is limited by technical (material properties, contamination risks, and the need for safety in food contact materials) as well as economic reasons. Mechanical recycling, which involves cleaning and reprocessing plastics, often results in lower-quality material that requires additives. Chemical recycling is an emerging alternative, but it can be limited to certain plastic types, be energy-intensive, and generate toxic waste. Further, chemical recycling approaches have not yet been proven to be sufficiently scalable. Despite these efforts, most plastic food packaging is either downcycled or not recycled at all, with PET bottles being a notable exception. Plastics that are not recovered for reuse or recycling are incinerated (waste to energy), landfilled, or littered.
The most common food contact materials (FCMs) used within foodware and packaging products are different types of , including , , , , and materials. These FCMs are used in combination with each other and with other materials, such as printing inks, adhesives, and coatings.
This is an important issue. Plastics dominate the food packaging market because they have many advantages: they are cheap, versatile, lightweight, with good protective qualities. While the exact percentage may vary across regions, plastics are estimated to account for 50 to 60% of food packaging products globally. Plastic-based food packaging is therefore a sustainability hot spot, with a disproportionate amount of the waste not being recovered ().
Primary food packaging impacts extend to human health because they are in contact with our food. Ensuring the safety and sustainability of packaging materials is essential for protecting public health. There is scientific evidence that chemicals in foodware and packaging materials can contaminate food and water sources, posing health risks. Chemically complex materials with low such as , , and are of particular concern.
➡️ But what exactly is ""?
are being marketed as eco-friendly alternatives to conventional plastics, offering both biobased and/or biodegradable options. However, they are not as straightforward a solution to the environmental and human health issues posed by traditional plastics as they might sound.
Ceramics are widely used in food contact applications due to their excellent resistance to heat, stains, and odors, making them ideal for cooking, serving, and storing food. The non-reactive nature of ceramics ensures that they do not affect the taste or quality of the food.
Ceramic food contact materials are made from natural minerals such as clay, quartz, and feldspar, which are molded and then fired at high temperatures to form a durable and non-porous surface. Ceramics are often coated with a glaze, which provides a smooth, glass-like finish and enhances their appearance and usability. The chemical composition of both the ceramic body and the glaze can vary, and the chemical safety of ceramics depends largely on the stability of these materials under typical usage conditions.
The safety of ceramic food contact materials is primarily concerned with the potential release of heavy metals, such as lead and cadmium, from the glaze into food, especially when the ceramics are used to store acidic foods or are subjected to high temperatures. The risk of such migration depends on the quality of the glaze and the firing process. Well-manufactured ceramics with stable glazes are generally very safe for food contact, but poorly made products or those intended to be only decorative may pose a significant health risk.
Ceramic materials are not recyclable in the same way as metals, glass, or paper, due to their rigid and non-melting structure. At the end of their life, ceramic items typically end up in landfills, where they do not degrade, contributing to long-term environmental persistence. However, due to their durability and resistance to wear, ceramics are often used for very long periods, reducing their frequency of disposal.
The comparison between single-use versus reusable food packaging options revolves around environmental concerns, cost, convenience, and specific use cases. When focusing on the environmental impacts of the packaging system, it becomes evident that the recoverability of packaging products is critical.
Recoverability is an integral part of the waste hierarchy, a conceptual framework ranking waste management options according to what is best to minimize resource use and waste. The waste hierarchy says that whenever possible, we should first rethink and redesign a foodware or packaging product (or the entire food delivery process) to actively prevent the generation of any waste or to reduce the amount of packaging needed.
Let's more closely evaluate the impacts of the two standard packaging systems:
The UP Scorecard measures the impacts of commonly used foodware and food packaging materials with a single yardstick. This free and comprehensive tool supports sustainable purchasing decisions for these products based on the latest available science. Scores are provided for , , , , , and .
Developed through an unprecedented collaboration of leading food service companies, NGOs, and technical experts called the, the UP Scorecard provides an authoritative resource for businesses as well as for environmental and human health advocates.
It then gives priority to closed-loop systems where, in a perfect system, 100% of the material originally used in a given packaging application is reutilized for the same application as many times as possible. In reality, no such thing as a fully closed loop exists (). However, the waste hierarchy indicates that some approaches are generally better in terms of circularity and resource efficiency. In this context, reuse is prioritized over recycling, composting, landfilling, and lastly, incineration ().
and associated recovery options
and associated logistics
Glass is an inorganic material that has been used to store and transport food and beverages for thousands of years. In modern food packaging, soda-lime glass is used. This type of glass is made up of sand, soda ash, limestone, and metal oxides. Glass bottles and containers usually require closures or lids made of other materials, such as metals, plastics, and cork.
Glass production has notable environmental impacts due to its high energy requirements (especially during the melting stage where raw materials are heated to over 1500°C), resulting in greenhouse gas emissions, and the potential ecological harm from raw material extraction. In addition, glass is a heavy material, which results in higher greenhouse gas emissions during transport compared to lighter packaging items.
Glass is an inorganic material composed primarily of silicon dioxide and metal oxides, forming a strong and durable network. This structure gives glass exceptional barrier properties, preventing the passage of even small molecules like oxygen and ensuring that no chemicals are absorbed from the contained food. Due to these properties, glass is chemically stable, making it a safe choice for food packaging with minimal risk of chemical migration from the glass itself. However, closures and lids, often made from other materials, can sometimes pose a risk of chemical transfer depending on their composition and the conditions under which the food is stored.
Glass is highly valued for its durability and recyclability. It can be reused many times without losing its quality, and it can be recycled indefinitely. The recycling process for glass, although energy-intensive, saves up to 25% of the energy required to produce virgin glass. Effective recycling requires careful sorting by color and exclusion of non-container glass types, like crystal or mirrors, which can contaminate the recycling process. Glass does not degrade in landfills, making it a persistent material. Its durability and ease of cleaning make it an excellent candidate for reuse, which significantly reduces its environmental impact compared to recycling.
If you want to learn more about glass, please visit the pages linked below.
Metal has been widely used as food packaging since the early 19th century. The invention of the canning process made it possible to not only store but also conserve food directly in the packaging. Metal food packaging, such as aluminum cans and steel tins, is primarily composed of metal alloys. Aluminum packaging includes over 90% aluminum with other metals like copper and zinc, while steel packaging is often tin-coated. Metal packaging is durable and offers strong protection against gases, light, and odors, which, combined with its ability to withstand high temperatures, makes it a popular choice for food storage and preservation.
The extraction and production of metals have several environmental impacts, including greenhouse gas emissions, emissions of other contaminants to air and water, and production of other waste. Metals are among the most recycled materials: the production impacts can be significantly reduced when scrap metal is reprocessed into new items.
At the end of its life, metal packaging has varied recycling possibilities. Aluminum and steel cans can be recycled repeatedly, preserving the quality of the metal. Recycling processes for aluminum involve shredding, removing coatings by heating, and melting the material to form new cans. Steel cans are separated magnetically, cleaned, and detinned before being melted and recast. Both materials' recycling processes are energy-intensive but significantly reduce the need for new raw materials compared to the production of virgin metals. However, items with thin metal layers, like beverage cartons, are often not recyclable due to technical and economic limitations.
Similar to glass, the durability, recyclability, and inertness of metals make them excellent candidates for reusable foodware and packaging.
If you want to learn more about metals, please visit the pages linked below.
Direct contact between food and metal can cause undesirable interactions, so some types of metal packaging are typically coated with organic polymers to prevent metal ions from migrating into the food. These coatings can release harmful chemicals, such as and other substances into the food. Stainless steel is one type of metal that does not require a coating and significantly reduces concerns for chemical migration.
Multimaterial food packaging combines layers of different materials to achieve specific protective functions. A typical example is the beverage carton, which contains about 75% paperboard for stability, 20% plastics (usually polyethylene) to prevent leaks, and up to 5% aluminum to protect against light, oxygen, and chemical migration. Other examples include pouches, tubes, and trays made from laminated films of plastic and aluminum, often found in the form of metal-coated cardboard. Adhesives and printing inks are also integral components, ensuring functionality and branding.
Multimaterial packaging, composed of two or more materials, can contribute to resource depletion and pollution. However, their main drawback is related to recycling difficulties (see below).
Chemical migration in multi-material packaging primarily depends on the material directly in contact with food. However, substances from outer layers, adhesives, or printing inks can also penetrate into food if no adequate barrier exists to prevent chemical migration. The phenomenon known as ‘set-off migration,’ can also occur during production when packaging materials are stored in reels (or final products are stacked inside one another), causing chemicals from the printed exterior to transfer to the food contact interior.
Multimaterial food packaging presents significant recycling challenges. Its layers, though thin, are difficult to separate, which complicates the recycling process. Beverage cartons, for example, can undergo fiber recovery during recycling by separating the paperboard from plastic and aluminum layers. However, the remaining composites are downcycled into lower-quality products like plastic pallets. Laminated films, made of plastic and aluminum, are even harder to recycle, and recycled materials from such packaging are not used in direct food contact, limiting the potential for closed-loop recycling.
Most multi-material packaging ends up being incinerated or landfilled. Efforts are growing to improve recycling technologies for this type of packaging, but the complete separation of materials and reuse in food packaging remains out of reach. This downcycling means that multimaterial packaging cannot yet contribute to a truly circular economy.
If you want to learn more about multi-material packaging, please visit the pages linked below.
Reusable foodware and packaging are designed for multiple uses, maintaining their quality and safety through many cleaning cycles. Their durability helps offset the environmental impacts of production, but their benefits depend on achieving enough reuses to offset the impacts from production compared to their single-use alternatives. This also includes the additional impacts from transport and washing cycles.
Water use is a key consideration, as reusable items need to be cleaned after each use. Efficient washing systems that recycle water can minimize this impact, particularly in areas where water is scarce.
Sufficiently scaled infrastructure also plays a vital role in enabling the proper functioning of reuse systems. This includes setting up refill stations or centralized washing facilities and ensuring efficient transport for collection and redistribution. Successful systems should be adapted to social and cultural contexts to encourage widespread adoption. Standardization across markets or sectors can also help streamline operations, reduce costs, and improve user convenience, making reuse both a practical and low-impact system.
In terms of chemical safety, durable and highly inert materials like glass, stainless steel, and ceramics tend to be most stable and do not interact with food or degrade over time. This is different from non-inert materials like most plastics, which can release chemicals with repeated use and washing.
Ensuring the long-term safety of materials is crucial, as is maintaining their recyclability at the end of their life. After many cycles of use, reusable products will eventually break or degrade, making recyclability important. Permanent materials like glass, steel, and aluminum can be recycled indefinitely, while plastic recycling is more limited due to material degradation. Some materials, such as ceramics, cannot be recycled at all.
If you want to learn more, explore the resources linked below.
Single-use packaging refers to packaging designed to be used once and then discarded. This type of packaging is commonly made from materials such as plastic, paper, aluminum, or composite materials and is widely used for convenience in food service, retail, and take-out industries.
Its primary benefit is its convenience - single-use packaging is lightweight, affordable, and readily available, making it easy to package, transport, and serve food and beverages. Depending on the material, single-use packaging is also a short-term, cost-effective option.
However, single-use packaging usually has significant environmental and health drawbacks. Many of these items are made from non-renewable resources, such as plastic derived from fossil fuels, and they are often not (or to a very limited extent) recycled or composted due to technical challenges (separation of components, material degradation, contamination of the materials), deficient collection systems, lack of facilities, economic aspects (lack of market opportunities for recycled material), etc.
This contributes to the accumulation of waste in landfills, oceans, and other environments, where single-use packaging can persist for decades or longer without breaking down. Additionally, the production of many single-use packaging often involves harmful chemicals, which can leach into the environment or pose risks to human health during use and at the end of life.
Despite its convenience, the environmental impacts of single-use packaging have led to growing concerns and calls for more sustainable alternatives. Many businesses and consumers are exploring options like reusable packaging, more compostable materials, and improved recycling practices to reduce reliance on single-use items or at least minimize their ecological footprint.
Paper and board have a long tradition as packaging materials. They are made of cellulose fibers that are mainly derived from wood. Paper and board are renewable and biodegradable materials. They are typically used as packaging material for dry foods, e.g., flour, rice, and pasta. In addition, they are broadly applied as secondary packaging, for example, cardboard boxes containing a plastic bag. Chemical treatments or combinations with other materials extend the application of paper and board packaging to liquid and/or fatty foods, making them functional candidates for takeaway food and beverage containers.
Paper and board packaging is made from cellulosic fibers, typically derived from renewable resources such as wood or bamboo. Virgin fibers are typically used for the production of primary food packaging, to maintain the desired mechanical properties, and to avoid cross-contamination issues from recycled paper streams containing all kinds of printed paper not intended for food contact.
Key environmental concerns associated with paper and board production are deforestation and energy and water consumption, as well as air, water, and land pollution (the pulp and paper industry needs various chemical inputs to operate). The impacts can be mitigated when using cellulose from certified sources (sustainable forestry) or when using alternative sources, i.e. from agricultural or food wastes, such as bagasse.
Paper and board products are often produced with various additives such as fillers, coatings, and synthetic binders. These materials are frequently printed, dyed, or glued, leading to a complex and often unknown chemical composition. Due to their porous nature, paper and board have low barrier properties, allowing chemicals from the packaging, including those from printing inks and adhesives, to migrate into the food.
To reduce chemical migration, strategies like using virgin fibers, internal bags, or barrier layers can be employed, but these can impact recyclability and environmental sustainability. This highlights the need to avoid hazardous chemicals throughout the production process of paper and board to ensure safer and more sustainable packaging.
If you want to learn more about paper & board, please visit the pages linked below.
Paper and board are increasingly used as alternatives to plastic, especially when coated or chemically treated to be waterproof or grease-resistant. However, such treatments, sometimes involving substances like per- and polyfluoroalkyl substances (), can compromise chemical safety, as all PFAS are highly persistent and many are harmful to human health.
At the end of their lifecycle, paper and board packaging can be recycled, though the presence of coatings, chemical treatments, or food contamination can limit this potential. While these materials are theoretically compostable, persistent chemicals like can spread into the environment through composting. During paper and board packaging production with recycled material, fresh fibers are usually added to maintain quality, and chemicals from the recycling stream may remain in the final product, potentially migrating into food.
The UP Scorecard scores the human health and environmental impacts of generic foodware and food packaging items that represent commonly used products in the food service industry. Products are scored in six impact areas (shown below), which are referred to as “metrics”.
The mix of quantitative and qualitative metrics used within the scorecard was developed through collaboration and consultation with many experts in the areas of environmental impact assessment, sustainable procurement, material circularity, chemical toxicology, and plastic pollution.
Life Cycle Assessment (LCA) is a scientifically accepted tool to assess and compare the environmental impacts of products and services over their entire life, i.e. from cradle to grave.
In short, materials are made from raw resources (like oil, ores, and plants), which are then transformed into technical materials (like plastics, metals, and paper). These technical materials are processed into parts or components that are later assembled into products. The products are then used by consumers before they are eventually disposed of or reused.
At each of these life cycle stages (production, use, disposal), energy and materials are consumed (resource input), and emissions to air, water, and soil are generated (waste output). Both inputs and outputs can have a direct impact on the environment and humans. These impacts can be quantified by metrics, such as the CO2 footprint (climate change indicator), water usage, or eco-toxicity.
To use LCA successfully, in particular when comparing the impacts of two different products, it is important to carefully define the functional units and the system boundaries that apply.
In the approach used by the UP Scorecard, the impacts from recycling (sorting, transport, and reclamation) are assigned to the product that makes use of the recovered material. When a foodware item is recycled into a new material or product, the impacts from recycling are assigned to the new product using the cutoff method. This method treats recycling impacts like a raw material supply system rather than as waste management. If recycling has lower impacts than making new materials, then products with recycled content will usually have lower impacts too.
When assessing the sustainability of foodware and food packaging, some important impacts that are hard to measure such as the circularity of a product and human toxicity, are poorly covered by conventional LCA indicators. To complement existing LCA indicators and account for these impacts, the UP Scorecard developed its own scoring approach with 3 new metrics:
A qualitative rating that recognizes sustainable forestry, agricultural production, and the use of post-consumer recycled content. This metric takes advantage of existing material certifications that promote sustainable resource management.
A qualitative rating that represents the likelihood for the product to be reused, recycled, or composted. This depends on the availability of recycling and composting infrastructure as well as the product design.
A composite qualitative rating that indicates (1) whether a product is free of chemicals of concern to be avoided based on human and environmental health hazards, (2) the quality of the information used to support such a claim, (3) the propensity of chemicals to migrate from the material into food, and (4) the interaction between food and material.
This guide provides an introduction to key aspects of the UP Scorecard's methodology. A fully detailed version of the methodology and data sources used for all calculations is publicly available in a .
3 standardized metrics are applied that measure impacts from production to disposal:
3 qualitative metrics are applied based on :
For the quantitative life cycle metrics used in the UP Scorecard (, , ), results are presented based on a foodware or packaging product in a standard size () that depends on the use case:
Water is a finite and critical resource. It is essential for life (drinking, irrigation), and the economy (energy production, industry). It is therefore critical to quantify water consumption, as an integral part of a comprehensive evaluation of a product's overall sustainability.
The UP Scorecard's Water use metric is a quantitative estimate of the consumptive use of surface and groundwater during the product's life cycle. This is commonly referred to as Blue Water Use, and is expressed in liters of water used.
Excessive water use can cause ecosystem degradation, including loss of biodiversity, soil erosion, and reduced river flows, which affect aquatic and terrestrial life. LCA quantifies how much water is used in the production, use, and disposal of a product, allowing us to understand the potential for resource depletion, and helps assess the broader environmental effects of water consumption on natural habitats.
Certain materials and products require large amounts of water during their production processes, particularly in raw material extraction, processing, and manufacturing. This is the case for bio-based plastics, natural fibers, virgin aluminum, and plastics.
The choice of packaging system also affects the water use of food packaging solutions. For single-use packaging, most of the water is used for the production phase. Reusables, in addition to the water required for production, need to be washed after each use. To minimize the water needed to operate a return-based reuse system, high-efficiency machines and the reuse of washing water can help to minimize water use. Keep in mind that in some geographic areas, water for washing may be a limited resource and result in higher local environmental impacts.
Indicator: Liters of consumed water
The tool calculates the absolute value for water consumption in liters, and a normalized score from 1 to 100 (100 being the best score):
The graphic below shows the water consumption impact calculated in the UP Scorecard for disposable plates and trays made of different materials, and a reusable plate used 30 times.
To assess water use by the product system, the UP Scorecard makes use of the methodology of the Global Water Footprint Standard (). It computes the “blue water footprint,” which reports the consumptive use of surface and groundwater throughout the product supply chain, including actions that result in the transfer of water between reservoirs. The blue water footprint is reported in units of physical volume of water consumed, and it does not reflect water scarcity or any other spatial or geographic factors of water use. Blue water also excludes natural rainwater for irrigation (“green water”) and ignores the emission of pollutants or contaminants into water (“gray water”). More details are provided in the detailed methodology under and .
Plastic pollution refers to the accumulation of plastic materials in the environment, particularly in oceans, rivers, and landfills, where they harm ecosystems, wildlife, and human health. Since plastics are not biodegradable, they persist in the environment for centuries, breaking down into smaller pieces called microplastics, which pose even more challenges.
The UP Scorecard therefore comprises a Plastic Pollution metric: a quantitative estimate of the mass of plastic that enters the environment due to the production, use, recycling, and disposal of the product.
Plastics are thrown away on a massive scale. They are durable materials that
do not biodegrade, and it can take hundreds of years to break down, partly into problematic microplastics. So when plastics end up in the environment, they are persistent polluters. They can be found in various ecosystems, from the bottom of the ocean to the top of mountains, and they are found in our bodies.
Littered plastic items can alter the environment in many ways: they are a threat to marine ecosystems (ingestion by marine life, entanglement), they can release toxic chemicals in water and soil, they clog drains, etc.
For these reasons, plastic waste is a sustainability hot spot, and plastic pollution is measured and evaluated in LCAs. The Plastic Pollution metric measures how much plastic ends up in the environment, including land and water areas.
Indicator: g of plastic leakage to the environment
The Plastic Pollution metric estimates the amount of plastic that enters the environment. It includes plastic pollution to land and aquatic ecosystems. Leakage from the following five life cycle stages is estimated:
Manufacturing and Transport: Small plastic pellets called "nurdles" can be lost during production and shipping.
Supply Chain: Plastic can be lost when it is turned into products, like containers.
Littering: Plastic can be discarded improperly before it is collected as trash. This is the biggest source of plastic pollution.
Waste Management: Plastic can be lost during recycling and waste sorting processes.
Export: Plastic can be lost when it is shipped overseas.
The tool calculates the absolute value for plastic leakage in grams, and a normalized score from 1 to 100 (100 being the best score):
The graphic below shows the grams of plastic leaked calculated in the tool, for disposable food containers made of different materials, and a reusable plastic container. The graph illustrates the potential for plastic pollution of a reusable item, according to how many times it is reused.
The UP Scorecard estimates leakage rates at each stage and reports the aggregate contribution to plastic pollution, in units of mass. Different plastic resins are assumed to leak at the same rate for a particular life cycle stage. As location-specific (e.g. state, county, or city) data representing litter rates and waste management practices become more available, the estimates of plastic leakage can be updated to account for these data. More details are provided in the detailed methodology under and .
The presence of toxic chemicals in food packaging associated with harm to humans and the environment is well documented. Hundreds of different harmful substances can be present in the various types of materials used in food packaging, and they can migrate in different amounts and at different rates depending on many factors.
Certain chemicals are linked to negative human health effects when consumed through this pathway - these are referred to as Chemicals of Concern (CoCs). You can download the CoCs considered with the UP Scorecard as defined by the .
Sustainable foodware must be safe for both the environment and humans. With this metric, the UP Scorecard helps to ensure this by considering whether foodware or packaging items contain CoCs, guiding users to avoid the most concerning substances and move towards healthier materials.
Food contact materials (FCMs) are used to make food contact articles (FCAs) that come into contact with food and beverages during, for example, processing, storing, packaging, or consumption. The chemicals within these FCMs and FCAs are known as food contact chemicals (FCCs).
FCCs are found in all food contact materials. Over 15'000 FCCs are known to be intentionally added substances (IAS; such as additives and processing aids). There can also be thousands (up to 100'000 according to some experts) of non-intentionally added substances (NIAS; such as impurities, contaminants, breakdown products, and reaction by-products) present in FCMs.
There is scientific evidence that many FCCs can migrate from foodware and packaging into foodstuffs: thousands of FCCs have been detected in migrates and extracts from food contact materials and articles.
FCCs can contaminate food when they migrate into the food, resulting in human exposure to complex chemical mixtures. Some FCCs have hazard properties defined as harmful. They are known as Chemicals of Concern (CoCs), and they can affect both the environment and human health in many different ways.
FCCs are present in FCMs, they can migrate into foodstuff, and potentially end up being ingested by humans. Various international biomonitoring programs, databases, and primary literature now provide evidence that hundreds of FCCs have been found in human bodies.
Considering the scientific evidence, reducing or eliminating CoCs from foodware and packaging is a critical step towards safer and more sustainable products and food systems. The CoC metric within the UP Scorecard is meant to guide decision-makers who want to improve their chemical safety standards for foodware and packaging.
Indicator: scale from 2 - 20
To provide a starting point and pathway to safer foodware and packaging, a matrix approach was developed that considers (1) the presence of chemicals of concern in the packaging material, and (2) the migration potential of chemicals in the food being packaged. These scores are then combined to calculate (3) an overall CoC score.
To evaluate the human health impact of a foodware or packaging article, the first aspect to address is whether there are any intentionally added and potentially harmful chemicals in a product. The UP Scorecard does this by asking users to check for these chemicals and then to disclose the reliability of this claim.
Compliance with the FCCprio List's tiers of priority chemicals can help suppliers and purchasers stay ahead of future regulations and consumer concerns. If a product does not intentionally contain any of the 1,200+ chemicals listed in the 4 tiers, it can get the highest score. If at least one chemical from tier 1 is intentionally present, the product gets the worst score. The score can be progressively improved by manually confirming that chemicals from tiers 1, 2, 3, and 4 are not intentionally used in the product.
The scorecard also rewards the disclosure level used to declare compliance with the FCCprio List. Users can declare different levels of disclosure that a product does not intentionally contain any of the chemicals in one or more of the tiers:
Beyond just containing a chemical of concern, another important aspect is the likelihood of the chemical migrating into the food (and exposing the consumer). This is directly linked to the inertness of the food contact material (material inertness) and to the conditions in which the food contact article is used (defining food and material interactions).
Beyond just describing the migration of intentionally used CoCs, considering the material inertness also helps to take into account the potential migration of many additional chemicals that can be present known as non-intentionally added substances (NIAS). These are often entirely unknown and untested chemicals present in a material as contaminants, degradation products, or reaction by-products from the production process. They too can have hazardous properties and threaten consumer health.
There is scientific evidence showing that the release of chemicals from foodware and packaging into foodstuffs is influenced by various factors characterizing the storage and usage conditions.
Such factors include storage time, temperature, fat content, acidity, as well as container size.
In the UP Scorecard, an example worst-case scenario with the highest food and material interactions (leading to the most chemical migration) would be a hot, oily, acidic soup served in a small cup. A pre-defined set of common foods is available in the scorecard for users to apply. Users can also create and save custom foods to use in their product comparisons by providing some basic information about the food's properties and storage conditions.
The overall CoC score combines the Presence Score and the Migration Potential Score as shown in Equation 1. This score is then linearly normalized to be within the range of 1 (worst) to 100 (best) so as to match the scoring range of the other five metrics.
The graphic below shows the default CoC score for a highly inert material (ceramic) and a less inert material (PP). The graphic also shows the influence of the foodstuff being packaged on the CoC score. In both cases, the default compliance score is assumed (meaning that CoCs may be intentionally used in both products). A user could manually improve the scores by confirming compliance with the FCCprio List based on a high disclosure level.
Sustainable sourcing is the first step towards circularity. The UP Scorecard looks at sustainable sourcing from the environmental performance point of view and focuses on the origin of the technical materials used to manufacture new food packaging and foodware items.
In general, renewable feedstock including bio-based raw materials and recycled raw materials are considered in the definition of sustainable sourcing.
With the Sustainable Sourcing metric, the UP Scorecard therefore considers how much recycled or bio-based content products contain and whether products have third-party certified sourcing practices.
Many experts interviewed for this project spoke to the importance of sustainable sourcing when considering the environmental tradeoffs of different packaging materials. Two priorities emerged from these discussions: increase the use of post-consumer recycled content and, for bio-based materials, reward sustainable agriculture and forestry practices.
In addition to reducing lifecycle water consumption and greenhouse gas emissions, mixing post-consumer recycled content into the packaging material closes the loop and creates demand for additional recycling while reducing the need to extract virgin materials.
Indicator: scale from 1 to 5
Sustainable Sourcing of a product is determined in the UP Scorecard by two factors:
Amount of post-consumer recycled content (PCR content)
The integration of PCR content into the production of food packaging items is not automatic. In the tool, certain materials contain by default a certain fraction of recycled material, reflecting the current maturity of different recycling industries (glass, metal, and PET are considered to be mature). Other materials have 0% PCR by default because they are currently not recycled at scale, for diverse reasons (usually technical or economical). This is the case for polypropylene (PP), polyethylene (PE), or polystyrene (PS). For certain materials, PCR content is not recommended for food contact articles due to cross-contamination issues (paper and board).
Certifications: sustainable agriculture and forestry practices for bio-based materials
The following third-party certifications are recognized to reward sustainable biomass production:
"Best" certifications:
"Good" certification
Considering these factors (amount of post-consumer recycled content; sustainability certifications for bio-based materials), a rating between 1 and 5 is given to a product according to the following criteria (ratings are then normalized to a score from 1/worse to 100/best):
The graphic below shows the Sustainable Sourcing score calculated in the tool, for disposable food containers made of different materials with varying PCR contents and certifications, and a reusable alternative.
Where only limited or highly uncertain data were available to inform the score, this is visually communicated to the user on the scorecard's results page. More details are available in the of the full methodology document.
Providing that the information is available (or can be obtained by talking with manufacturers or suppliers), users can compare the chemicals intentionally used in manufacturing a product with the Food Packaging Forum's .
The release of chemicals into food depends on the inertness of the material, which describes how possible it is for chemicals to move into and out of the material. Some materials are endowed with extremely high barrier properties (they do not let any chemical through), while other more porous materials have very poor barrier properties. In the UP Scorecard, generic food contact materials were scored by scientific experts from very low to very high migration potential (see Section 4.5 of the for details).
The PCR content of a product can be adjusted by the user (see section).
Most bio-based products in the tool are by default not made from certified raw materials. The user can adjust these settings (see section).
Overall, data to perform calculations were collected from several sources:
Direct Measurements. Measuring mass and size (volume and/or area) of many different, real market products
Published literature including peer-reviewed scientific journal articles, published government reports, and industry publications.
Life cycle inventory databases. Where possible, the internationally recognized Ecoinvent database is used to model the life cycle of products. Other sources were used to model materials or processes that are not included in ecoinvent.
Interviews with experts in toxicology and chemicals, life cycle assessment, recycling, and waste management, and food service operations.
While the UP Scorecard can be used as a guest without registering, creating an account for free is recommended in order to access all features, such as saving custom products & foods, comparison results, and portfolios.
Name, Email, Password, Company/Organization, and Job Title are mandatory fields. Optionally, we also ask you to give us some additional information about your work and what you wish to accomplish with the UP Scorecard. This will help us improve the tool further in the future. You can also subscribe to our newsletter to learn about future training opportunities and updates.
Use Portfolio Scoring to score an entire custom portfolio of different products and use cases:
On the results page, you will see a table displaying your portfolio's score, as well as the best and worst alternative portfolio. Below that you will find the cumulative raw scores for your portfolio. Individual values for each product can be seen by switching the toggle to Score per Use of Product. Furthermore, we provide you with some circularity details and KPIs on your portfolio, as well as details of your portfolio and individual products.
Product comparison mode compares products that provide the same service. For example, you can compare different types of beverage containers:
In portfolio scoring mode, you can assess an entire product portfolio:
You can compare this portfolio to the Best and Worst portfolios (automatically generated by the UP Scorecard).
The Best and Worst portfolios always provide the same service and serve the same foods (or beverages) as your portfolio. But they only include the best-scoring (conversely the worse-scoring) products.
On the other hand, the UP Scorecard allows you to add and compare any other portfolio you have created, regardless of the types of services they provide. This comparison is likely to be most useful when the two portfolios provide the same use cases and number of uses.
The UP Scorecard assesses generic foodware and food packaging types and assumes a set of default settings. The tool offers many possibilities to change some of these default settings (but not all), allowing you to consider your local conditions, and to align the scoring with your business needs.
Use Product Comparison to score and compare products within the same use case. Use the tutorials below to learn how to generate a scoring sheet with the comparison mode.
On the results page, you will see a table displaying the different foodware and food packaging items you selected. For each item, the different scores for the six metrics are given, together with a summary score (unweighted average of the 6 metrics). Below the Comparison Scores, we provide you with some circularity details on the selected products. Below that, you will find all the details of each product (size, reusability, components, materials, and mass).
The UP Scorecard has various built-in products. However, if you cannot find the product you are looking for, there is an option to create a new product.
Creating a new product starts with providing two basic pieces of information:
Is the product a reusable item or a single-use item? If you have a reusable item, you will need to provide information on the reuse system in later sections.
Customization possibilities cover various topics, and they affect different metrics and scores. You have the opportunity to adjust the following:
What can you NOT customize?
Many parameters can be adjusted by the user in the tool, but not all of them. The table below shows what cannot be customized in the tool.
The calculations in the UP Scorecard were reviewed and programmed by a team of independent LCA professionals. Where possible, life cycle impact assessment calculations were carried out based on peer-reviewed inventory data managed within the internationally recognized database. A wide range of the most recent and publicly available data sources from governments, industry, academia, and NGO research and reporting projects were reviewed to inform model inputs including developing the life cycle inventory. Best professional judgment compiled from the multi-stakeholder experts involved in the tool’s development was applied to address data gaps and recognize uncertainties. All calculations, assumptions, and data sources are explained in detail in the .
"Climate Change is the defining issue of our time and we are at a defining moment. From shifting weather patterns that threaten food production, to rising sea levels that increase the risk of catastrophic flooding, the impacts of climate change are global in scope and unprecedented in scale. Without drastic action today, adapting to these impacts in the future will be more difficult and costly." - United Nations, on climate change as a global issue.
Because the current and future impacts of climate change are catastrophic, this phenomenon is logically a focus for sustainability reporting, and the UP Scorecard includes a Climate metric: a quantitative estimate of the life cycle global warming impact of the product.
Climate change is driven by greenhouse gas (GHG) emissions like carbon dioxide (CO₂), methane (CH₄), and nitrous oxide (N₂O). LCA helps track these emissions, from the extraction of raw materials to production, use, and disposal. These processes include raw material production, container manufacturing, delivery to a food service facility, use, washing (for reusable products), waste collection, landfilling, incineration, sorting, reclamation, and recycling. This provides a clear picture of a product’s contribution to climate change and enables efforts to reduce carbon footprints.
The choice of packaging material is important. Materials with the highest Global Warming Potential (GWP) are generally those that require significant amounts of energy during extraction, processing, and manufacturing, and those that rely on fossil fuels for production. Some materials with particularly high GWP are metals, plastics, and glass.
The choice of packaging system also affects the climate impact of food packaging solutions. For single-use packaging, most greenhouse gas emissions are associated with the production phase, and the ability of recycling at end-of-life to prevent the use of virgin materials. The greenhouse gas emissions associated with a reusable product are highly correlated to the energy and resource intensity required for production and cleaning, its weight in combination with the mode and distance it is transported, and the ability of recycling at end-of-life to prevent the use of virgin materials. Unlike single-use products, reusables require additional transport and washing cycles that should be considered to minimize climate impacts.
Our society cannot afford to waste natural resources on a crowded planet and with limited amounts of them. Efficient product and material recovery is also a core principle of the circular economy. We need to change our food system to use fewer disposable and hard-to-recycle products and focus on packaging that can be reused, recycled, or composted. Products that can safely do any of these are critical for a sustainable and circular economy.
The UP Scorecard Recoverability metric is a qualitative rating that represents the likelihood for the product to be reused, recycled, or composted. This depends on the availability of recycling and composting infrastructure, and on the product design.
In the UP Scorecard, the following end-of-life (i.e. recovery) scenarios are considered:
Reusable means a product is not created with the intent of disposal after a single use, is not conventionally disposed of after a single use, and is manufactured to withstand multiple washes and uses before it reaches the end of its useful life.
In the tool, the user can specify if a product is reusable; a product is considered reusable if it undergoes at least 5 use cycles.
Compostable means all the materials in a product or packaging are capable of undergoing biological decomposition in an appropriate (i.e., commercial or municipal) compost facility as part of an available program in a safe and timely manner (no more than 180 days), such that the material is not visually distinguishable and breaks down into carbon dioxide, water, inorganic compounds, and biomass suitable for use as a soil amendment (e.g., compost, soil-conditioning material, mulch), leaving no toxic residue.
Similar to the recycling challenges, composting requires a set of conditions:
Proper collection and sorting processes
Proper design for composting feasibility
Access to proper infrastructure
Recycling is a recovery operation by which waste materials are reprocessed into products, materials, or substances whether for the original or other purposes.
Recyclable vs. recycled: while many materials are deemed and labeled as recyclable, it does not mean that they will be effectively recycled. Efficient recycling only happens when several conditions are met:
Proper collection and sorting processes
Proper design for recycling feasibility
Access to dedicated infrastructure
In some very limited cases, a littered packaging item may be considered recoverable in the natural environment, i.e. it is converted to a beneficial material by natural processes. This is the case for fiber, paper, and cardboard-based materials without plastic lining and harmful chemicals such as PFAS.
In case the preferred end-of-life scenarios are not eligible, disposable food packaging usually ends up as waste. It can then be land-filled, incinerated, or littered, i.e. it is not recoverable. Regional statistics determine the recovery mix of land-filling and incineration. Incineration facilities often recover heat for energy, but their operation relies on fees from waste generators. Impacts from incineration are assigned to the product being burned using the cutoff method.
Indicator: scale from 1 to 5
Each material class has a score that applies if the material is recovered (recycled, composted, etc.) and another score if the material is sent to disposal (landfill or incineration).
Considering these factors, a rating between 1 and 5 is given to a product according to the following (ratings are then normalized to a score from 1/worst to 100/best):
The graphic below shows the Recovery scores calculated in the tool for disposable and reusable cups made of different materials.
Go to and launch the UP Scorecard tool. Alternatively, go to directly.
Currently, users can choose between Global, Europe, United States, Spain, and the imaginary . This represents the region where the products will be used. More regions might be added in the future.
Learn how to customize recovery settings .
If you want to know why it is important to input what foodstuff or beverage is being served or packed, please read the section on .
Select at least two products. One of them must be a reusable option. Press Create Portfolio to continue. If you are logged in, you also have the option to to add to the comparison in this step.
From here on you will be able to add new products to your portfolio, edit details of your products, , and view your portfolio's score.
The UP Scorecard offers two different scoring pathways: and .
The scores for , , and are calculated for a (e.g. 1 liter of beverage served). The qualitative metrics (, , and ) are based on the material values set by default or on customized properties set by the user.
The scores for , , and are calculated for all products in the portfolio (e.g. 10 x 250ml cups). The qualitative metrics (, , and ) are based on the material values set by default or on customized properties set by the user.
Customization possibilities cover various topics, and they affect different metrics and scores. You can explore what you can customize in the next section , and you can learn how to customize in the section .
Currently, users can choose between Global, Europe, United States, Spain, and the imaginary . This represents the region where the products will be used. More regions might be added in the future.
Learn how to customize recovery settings .
If you want to know why it is important to input what foodstuff or beverage is being served or packed, please read the section on .
Select at least two products. One of them must be a reusable option. Press Create Comparison to view your results. If you are logged in, you also have the option to to add to the comparison in this step.
In the Product Comparison mode, scores will be calculated for the volume an item carries (see for more information).
Here, you also have the option to .
What is the total volume (or area) provided by the product? The capacity (volume or area) of a product is important to defining the in the tool.
The Climate indicator estimates the mass of carbon dioxide equivalent emissions of the product and is assessed using the IPCC 2013 radiative forcing factors as implemented by the Ecoinvent Centre. The implementation includes 45 substances characterized in terms of their relative radiative forcing potential in comparison to CO2. More details are provided in the detailed methodology under and .
The tool shows the absolute value for GHG emissions in and a normalized score from 0 to 100 (100 being the best score):
For these reasons, the tool lets the user specify if all those conditions are met (see ).
In many regions, those conditions are not met, and many theoretically recyclable items end up as waste. For these reasons, the tool lets the user specify if all those conditions are met (see ).
The Recoverability metric is a qualitative rating that represents the potential for the material to be reused, recycled, composted, or turned into something useful by nature. This metric considers compostability, packaging design for recyclability, and material persistence. All materials are ranked in one of five performance tiers (see below). The tiers, and placement of materials within the tiers, were developed through interviews with experts outside the project team. More details are provided in the detailed methodology under .
the product’s design is “” for recovery, and
Life Cycle Model
Introduction to the ecoinvent database
Methodology: Climate Impact
Methodology: Recoverability
Safe and environmentally sound purchasing decisions for foodware and packaging become the norm when (1) their impacts on human health and the environment are transparent and easy to assess, and (2) when choices that reduce these impacts are more incentivized. But the lack of technical expertise, transparency, and/or time in the procurement of foodware and packaging currently makes sound decision-making difficult. Therefore, the UP Scorecard makes responsible packaging decisions easy and intuitive to help make the right product choices for procurement and beyond.
The impacts of producing the product (raw materials, forming, and transport) depend on the region of production. The region of use determines the average rates of recovery, recycled content inclusion, and disposal mixes.
By default, the region of production is set to be the same as the region of use. But the users can specify the region of production for a product, distinct from the region of use.
For the customizable transportation legs, the users can choose between different transportation modes, and specify the transportation distances. It is also possible to add transportation stages.
Reusable packaging systems require complex logistics involving pick up, return, sanitizing, and redistribution of the containers.
The migration of chemicals from foodware and packaging into food increases when the type of food has:
Long storage times
High temperature
High acidity
High fat content
High contact with material
Small packaging ratio
In the tool, the user can select from a list of predefined foods and beverages. If no food is selected, the tool assumes the worst-case scenario: a hot, fatty, and acidic soup, stored for a long time, in a small container.
When evaluating the health impact of a food packaging item, the UP Scorecard essentially considers the presence of hazardous chemicals and whether they are likely to migrate from the food contact material to the food or beverage content. In more detail, the following criteria contribute to the final COC score:
What is the disclosure level for the compliance statement?
Migration potential: How inert is the material?
Food/material interaction: How do the container and food interact?
By default, the UP Scorecard considers that all food contact materials contain at least one chemical of concern from Tier 1.
The utilization of renewable feedstock (i.e. bio-based raw materials) or recycled raw materials can contribute to reducing environmental impacts. Here is what you can customize in the UP Scorecard.
In the UP Scorecard, a product is considered to be effectively recovered if it is reused, composted, or recycled, which means that a product fulfills the following:
recoverable, i.e. designed for reuse, recycling, or composting, and
collected and processed, i.e. the infrastructure to reuse, recycle, or compost the specified product is available.
your product is designed for optimal composting or recycling
you have access to the infrastructures that can properly handle the composting or recycling of this product
If both conditions are fulfilled, then the product is considered recovered and the recovery score can improve. Below are the composting and recycling settings that can be customized.
If you serve a specific food or beverage, you can define it in the tool and use it in your assessment.
Activity impacts
Regionalized data: 4 regions available (Global, USA, Europe, )
Retrieved from different sources (see )
Inertness
Defined for all materials: see tables and in methodology
Average recovery rate
Regionalized data: 4 regions available (Global, USA, Europe, )
Applies only when Recovery toggle is set to “Default” position (see )
Disposal mix
Regionalized data: 4 regions available (Global, USA, Europe, )
(for unrecovered materials)
Various transport processes throughout a product life cycle contribute to environmental impacts. Some transport stages are embedded within predefined activities and cannot be modified by the users (see default values for ), while others may be customized:
Finally, the user can adjust the (default is 85%).
The transportation parameter strongly influences the climate metric. The graph below shows how the changes based on transportation modes for different materials. The following graph shows the life cycle global warming impact of various single-use items, with different supplier-to-user transportation scenarios (values in ).
The number of uses for a reusable product is key to achieving potential environmental and circularity gains when compared to single-use packaging. The UP Scorecard provides a baseline value for different reusables, based on expert consultations: see .
When creating a new reusable product or when customizing a reusable product, the user can adjust this parameter to reflect their real situation.
The environmental impact of reusables depends on the conditions and efficiency of the repeated washing cycles. The tool lets you adjust the washing logistics system and the washing loads.
Washing logistics system
The collection, return, and washing of reusables may be on-site, or off-site. In the latter case, transport from the point of use to washing facilities is needed. Users can specify which type of logistics system is available in their context, and adjust the transport distance in case they choose off-site options (transport mode is assumed to be by truck).
Washing load
You may create a new food or drink type by selecting the values for these factors that most accurately describe your use case. More information on the Food and Materials Interactions can be found . More detailed information can be found in the .
See .
Compliance statement: are there any chemicals of concern, that are intentionally added during manufacturing? We provide a . The chemicals of concern within this list are prioritized and grouped into four tiers, where Tier 1 presents a shortlist of priority chemicals of concern to avoid, and Tiers 2, 3, and 4 present more extensive sets of chemicals that should not be used in the manufacture of food contact materials.
Compliance statement
Intentionally contains at least one COC identified in Tier 1
Yes
If the user has any information about the intentional utilization of COCs, they can declare compliance with one or more COC tiers.
Disclosure level
Supplier is unable to provide information about in-scope chemicals of concern in the materials within the foodware or packaging component
Yes
The user can support their compliance statement with different levels of reliability (from self-declaration to third-party verified declaration).
Inertness
Glass, steel & ceramic: best score All other materials: lowest score
No
See explanation.
Food and material interaction
Worst case food: hot, oily, acidic soup
Yes
Users may either select one of the predefined food or drink options, or create their own (see )
The Chemicals of Concern information can be changed when or .
Post-consumer recycled (PCR) content is predefined for all materials and products in the tool: see (note that it is region-dependent). Some materials contain PCR by default, while others do not.
The user can change the PCR content for a product when creating a new product and when customizing an existing product.
Bio-based materials are by default not certified. The user can add certifications demonstrating commitment to environmental and social sustainability practices, including:
"Best" certifications:
"Good" certification
Currently, the tool only considers certifications for bio-based materials.
Except for a few products and materials for which mature recovery systems are in place, the tool considers that products are not designed for recycling or composting and that the infrastructure is not available. For materials considered recoverable, are used.
It is therefore up to the user to adjust settings for composting and recycling to reflect their local situations (see ) The tool lets you specify whether:
All materials are by default not compostable.
You can change the compostability when creating a product or customizing an existing product, by specifying if the product is certified as compostable, according to the following labels:
CMA Commercially Accepted Products List
BPI (BioProducts Institute)
Availability of composting facilities: by default not available.
If your municipality is equipped with an industrial composting center, you can specify this in the tool. This can be done on the result dashboard page or when editing a portfolio.
Only are considered optimized for recycling by default, reflecting the maturity of recycling chains (glass, aluminum, steel, and bottles and jugs made from #1 PET and #2 HDPE). You can change this when creating a product or customizing an existing product by specifying if the product is optimized for recycling or not.
Available by default for (most common ones: glass, aluminum, steel, and bottles and jugs made from #1 PET and #2 HDPE, and uncoated paper and board)
All other materials: by default not available
If your municipality is equipped with facilities that can process certain types of materials outside the most common ones, you can specify this in the tool on the result dashboard page, or when editing a portfolio.
Learn why this matters for your final scores .
In the tool, default values for the number of items fitting on standardized industrial washing machine racks are defined (see ). The user can adjust these numbers when creating a new product.
The UP Scorecard has various built-in products. However, if you cannot find the product you are looking for, there is an option to create a new product.
You will have to give your product an appropriate name and description. You can choose an existing product to base the new product on - or leave it empty and create a new product from scratch.
Choose whether the product is reusable or single use and define the product's volume. The UP Scorecard uses the full volume of a container, i.e. the volume of water when filled to the brim.
When applicable, set the recycled content percentage. Whether recycled content is allowed can be defined in the next section when defining custom product components.
The products are defined by their components. A product can comprise one or more components, and each of them needs to be described.
The UP Scorecard considers a component as part of the packaging or foodware that is designed to be separated by the user (e.g. a lid or a removable label or a protective sleeve).
When creating a new product, the user is invited to provide several parameters for each component:
The type of component
The type of material it is made of
The material weight
The litter class: the litter class depends on the size of the items. Small items have a higher litter rate than larger ones.
Here is a simplified example use case to better illustrate how to use the UP Scorecard in practice.
Here is an overview of the relevant plastic products used in the restaurant
Hot take out
Hot soup
Single-use polypropylene (PP) plastic container
15'000
Utensils
Hot soup
Polylactic acid (PLA) fork
15'000
Cold cups
Soda
Single-use clear polystyrene (PS) plastic cup
15'000
Straws
Soda
PP straw
15'000
Further details can be viewed in the Portfolio Dashboard.
Tutorials showing how to change settings and customize your assessments:
Reminder: to be considered recovered, a product must be recoverable and the recovery facilities must be available.
The tutorial below explains how to adjust these two settings.
To customize recovery infrastructure access, toggle Custom Composting and Recycling when comparing products or scoring a portfolio.
Now, choose the recovery options for the relevant products. Note that only certain materials are eligible for composting and recycling.
The availability of composting and recycling infrastructure can drastically change a product's overall score, as seen in the example below.
For Reusable products, define the and the wash system.
Mass: The mass is relevant when estimating carbon emissions during transportation for the metric.
Litter Class: Littering is relevant for the metric. The litter rate depends on the size of the items. Small items have a higher litter rate than larger ones.
Optimization for recycling and certifications are relevant to assess the and metrics.
Certifications: More information on the available Certifications can be found and .
The chemical tiers are available .
The physical characteristics of these components are predefined for existing products in the tool (see ). Below is an example:
The level of food contact: the interaction between food and material affects the Chemicals of Concern score (see more details ). If no food contact, the component does not affect the score. With incidental contact with food, the component contributes 10% to the score.
Using the , the above portfolio gets a Summary Score of 21/100 and amounts to a total emission of 3'227'649 g CO₂-eq and 8'659.74 g of plastic leakage.
For users who intend to go above and beyond, the UP Scorecard suggests a Best Alternative Portfolio. This is auto-generated and provides the same service and serves the same foods as the provided portfolio, but it only has the best-scoring products, according to the Summary Score in mode.
Alternatively, you can now save the portfolio and start a new to find better alternatives for each use case.
Having assessed and found more suitable alternatives, you can edit your initial portfolio and remove/add products based on the assessment in the mode. Now look at the new portfolio scores and see how much plastic leakage or greenhouse gas emissions could be saved by switching to more sustainable alternatives. Compare different portfolios to see where the impact of alternative products are biggest.
You can create new custom products and edit an existing product, either from the Results screen in or from the Edit Portfolio screen in .
Follow the same steps as when .
When editing an existing product, you will additionally have the option to customize . This option is not available when creating a new product.
The full is available where you can see the names and CAS (Chemical Abstracts Service) numbers of all chemicals included. Avoiding the intentional use of all PFAS (per- and polyfluoroalkyl substances) is required to reach Level 1 compliance within the Chemicals of Concern metric. Read the full for more information about how to use this list to increase a product’s score in the tool.
For the quantitative impact metrics (climate, water use, and plastic pollution), the UP Scorecard primarily makes use of life cycle inventory data from the highly respected database. Where necessary, custom inventories were defined (for a material or a process) and implemented using ecoinvent processes. In a few cases, the tool relies on , and in one case it uses (developed by the Argonne National Laboratory). For the qualitative metrics (chemicals of concern, recoverability, and sustainable sourcing), custom methodologies were developed and reviewed by groups of experts and based on recent scientific literature. See the full for more information about how each of the metrics are calculated.
The UP Scorecard is being developed by SUM’D, which is a fiscally sponsored project of , a registered 503(c) non-profit organization registered under United States law. The UP Scorecard is being hosted by the . Life cycle assessment (LCA) services are being provided by , and technical development of the tool is carried out in cooperation with . The UP Scorecard uses as a data source.
Ongoing development of the UP Scorecard is being made possible through the generous financial support of the and . Additional financial support has been provided through in-kind donations.
The first version of the UP Scorecard was produced by , with support from the Food Team at Google. The Lexicon’s accelerator programs bring together food companies, NGOs, scientists, entrepreneurs, and food producers from across the globe to tackle some of the most complex challenges facing our food systems, from regenerative agriculture to food is medicine.
This can be done when or .
"Trashtown" offers no recovery infrastructure, while "" has all the options. The score won't change for reusable products.
Creating a new product
Customizing an existing product
Creating a new foodstuff