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Agriculture & Future Food Systems · Article

Packaging, refrigeration and avoided losses

Compare the added resources used to protect food with the suitable food actually delivered, keeping avoided-loss and avoided-production assumptions explicit.

Preparation and related reading

Shared Foundations

Related articles

This article helps you

  • Connect protection with the actual deterioration route and food use.
  • Keep added burdens separate from justified avoided-production credits.
  • Test how a missing substitution changes a bounded comparison.

Start with the food-protection question

Imagine tender produce reaching its destination damaged. A different package or cooling arrangement might help, but it also requires material or energy. The useful question is whether the whole arrangement provides the specified suitable food with acceptable requirements.

Packaging can protect against a particular transfer while changing airflow or end-of-use handling. Refrigeration must suit the actual crop and process. Colder is not universally better, and protection does not retrospectively certify the safety of an affected lot.

Define the common food outcome

Compare arrangements serving the same stated food function, quantity and quality at the same endpoint. If one merely ships more damaged food, its lower packaging mass does not establish an equivalent result. Keep useful output and separately recorded unsuitable fractions visible.

Detailed preservation conditions and equipment design belong in their own topics. This article connects those processes with resource accounting. The boundary should include relevant protection, handling and destination processes rather than only the visible package.

Distinguish two avoided quantities

Food not discarded and food production displaced are different outcomes. A protection change can leave more existing food available, but the producer or consumer may not reduce another purchase or production step. An avoided-production credit needs an explicit substitution scenario and evidence appropriate to the question.

Keep additional packaging, electricity and end-of-use processes alongside any justified credit. Do not subtract kilograms of plastic directly from kilograms of food and call the difference an environmental benefit. They are different materials providing different functions.

Calculate a stipulated burden change

An original simplified scenario compares the same suitable-food use. Stipulate an added protection burden of 3 kg CO₂e, and that 10 kg of another food’s production is genuinely displaced at an invented 2 kg CO₂e/kg factor on a matching modelling basis. All other differences are excluded by assumption.

The modelled credit is 20 kg CO₂e, making the included change 3−20 = −17 kg CO₂e. The negative sign means a lower amount relative to this scenario’s baseline, not that the package removes carbon or that an actual intervention achieved the result. The diagram also shows what happens with no displaced production.

The substitution assumption changes the modelled result

The substitution assumption changes the modelled resultOriginal limited same-function comparison: extra protection 3 kg CO₂e; one scenario credits 20 kg CO₂e for stipulated displaced production, the other credits 0. Changes are−17 and+3 kg CO₂e. Original hypothetical difference model, no physical scale, actual emission factors, safe-preservation recipe or guaranteed avoided production.Added burden: 3 kg CO₂eAll other differences excluded byassumptionStipulated credit: 20 kgCO₂e10 kg displaced × invented 2 kgCO₂e/kgChange: −17 kg CO₂e3−20 relative to specifiedbaselineSame burden: 3 kg CO₂eSame protection, different useassumptionNo displacement credit: 0No avoided production isstipulatedChange: +3 kg CO₂e3−0; not a complete environmentalresultsubtractcreditincludedresultsubtractcreditincludedresult
Original hypothetical difference model, no physical scale, actual emission factors, safe-preservation recipe or guaranteed avoided production.
Read the diagram as text

Original limited same-function comparison: extra protection 3 kg CO₂e; one scenario credits 20 kg CO₂e for stipulated displaced production, the other credits 0. Changes are−17 and+3 kg CO₂e.

Parts

Added burden: 3 kg CO₂e
All other differences excluded by assumption
Stipulated credit: 20 kg CO₂e
10 kg displaced × invented 2 kg CO₂e/kg
Change: −17 kg CO₂e
3−20 relative to specified baseline
Same burden: 3 kg CO₂e
Same protection, different use assumption
No displacement credit: 0
No avoided production is stipulated
Change: +3 kg CO₂e
3−0; not a complete environmental result

Connections

  • Added burden: 3 kg CO₂e → Stipulated credit: 20 kg CO₂e: subtract credit
  • Stipulated credit: 20 kg CO₂e → Change: −17 kg CO₂e: included result
  • Same burden: 3 kg CO₂e → No displacement credit: 0: subtract credit
  • No displacement credit: 0 → Change: +3 kg CO₂e: included result

Test the assumption that controls the result

With the same added burden but zero displaced production, the included change is +3 kg CO₂e. The two results depend on a stated difference in substitution, not on changing the package’s physical properties. Neither is a full environmental assessment.

At the stipulated 2 kg CO₂e/kg factor, displacing 1.5 kg production would balance the 3 kg CO₂e added burden in this deliberately limited model. This is a mathematical threshold, not a recommended loss target or a real product result. Uncertainty in factors or other processes would change it.

Check use and other effects

Verify whether protected food reaches a suitable use and whether the proposed substitution occurs. Consider cost, work, material recovery and other environmental indicators. A climate-indicator improvement can coexist with an increase in another burden.

For the tender produce, assess the actual damage mechanism and workable protection first. Report the food outcome, added requirements and justified comparison. Less packaging and more protection can each be useful in appropriate conditions; neither label settles the overall tradeoff without evidence.

Worked examples

Calculate the included scenario change

Original matching-function scenario: added protection 3 kg CO₂e; explicitly displaced production 10 kg at an invented 2 kg CO₂e/kg factor. All other differences excluded.

  1. Displacement credit = 10×2 = 20 kg CO₂e.
  2. Included change = 3−20 = −17 kg CO₂e relative to baseline.
  3. This assumes actual substitution and a common modelling basis, not an observed intervention.

A 17 kg CO₂e reduction within this stipulated calculation; no full-life-cycle or empirical benefit proved.

Change only the credit assumption

The same added protection is 3 kg CO₂e, but displaced production is zero. What result and balancing quantity follow in the limited model?

  1. With zero credit, change = +3 kg CO₂e.
  2. At the invented 2 kg CO₂e/kg factor, balance requires 3/2 = 1.5 kg displaced production.
  3. That threshold excludes all other differences and factor uncertainty.

The zero-substitution case adds 3 kg CO₂e; 1.5 kg displacement would balance it only under the stated simplified assumptions.

Check your understanding

  1. Does food not discarded prove equal-mass food production avoided?

    Show answer and reasoning

    No.

    Actual substitution and the chosen comparison need evidence.

  2. Can packaging kilograms be subtracted from food kilograms as an impact benefit?

    Show answer and reasoning

    No.

    Different materials and functions require an appropriate common assessment method.

  3. Does a negative scenario difference mean the package physically removes carbon?

    Show answer and reasoning

    No.

    It indicates a modelled change relative to the specified baseline.

Key ideas

  • Compare the same suitable-food function and endpoint.
  • Keep protection burdens and substitution credits distinct.
  • Test controlling assumptions and other outcomes.

References

Sources supporting the explanations and examples in this article.

  1. Small-scale postharvest handling practices: temperature and relative humidity controlLisa Kitinoja, Adel A. KaderReference guidefao.orgRead source
  2. ILCD handbook: General guide for life cycle assessment, detailed guidance (2010)European Commission Joint Research Centre, Institute for Environment and SustainabilityReference guide · PDFpublications.jrc.ec.europa.euRead source
  3. From Field to Bin: environmental impacts of US food waste management pathways (Part 2)Shannon Kenny, Jenny Stephenson, Alexandra Stern, Juliana Beecher, Ben Morelli, Andrew Henderson, Emelyn Chiang, Andrew Beck, Sarah Cashman, Emily Wexler, Kyle McGaughy, Abby MartellReference guide · PDFepa.govRead source