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Agriculture & Future Food Systems · Article

Trade-offs and Transparent Dashboards

Compare food-system outcomes side by side,with useful output,system boundaries and missing evidence visible instead of hiding them inside one score.

Preparation and related reading

Shared Foundations

Related articles

This article helps you

  • Distinguish resource totals from amounts per useful output.
  • Present access, livelihoods, safety evidence and environmental measures together.
  • Explain how exclusions, weights and missing records affect a summary.

One improved number leaves other questions

A vegetable packing service reports lower electricity per delivered kilogram. That can be a real improvement on its stated basis, yet its total electricity might rise and customers might pay more. A food system has several relevant outcomes; no single resource ratio describes them all.

A trade-off arises when an option improves one relevant outcome while worsening another. Some combinations improve several outcomes together. Begin with the decision and affected people, then choose a compact set of measures that can reveal both possibilities. The purpose is comparison, not a display containing every number the organisation holds.

State the useful output and boundary

For a resource comparison, define the product, function, time and location. A kilogram of packed edible vegetables delivered in usable condition is different from a kilogram entering the warehouse. Product mix, storage duration and service requirements can also change what the denominator means.

Specify which stages are included. A facility electricity meter excludes some upstream production, transport and equipment impacts. An included refrigeration stage must retain its actual operating period. The comparison can still be useful at that limited boundary, provided it is not presented as a complete environmental ranking.

Read the total beside the ratio

In an invented comparison, the same defined packing-service boundary records 800 kWh for 1000 kg delivered in period A, and 900 kWh for 1500 kg in period B. Equivalent delivered product function is stipulated. Electricity intensity is 0.8 kWh/kg in A and 0.6 kWh/kg in B, a 25% decrease. Total electricity rises by 100 kWh, or 12.5%.

Both findings are correct. The lower ratio does not mean lower total demand. It also does not establish the intervention's effect, because the periods may differ in conditions. Nor does it establish emissions, cost or full-system sustainability: those questions require the electricity origin, other resources and relevant outcomes.

Invented facility records with one delivered-product basis
MeasurePeriod APeriod B
Delivered product1000 kg1500 kg
Included electricity800 kWh900 kWh
Electricity per delivered mass0.8 kWh/kg0.6 kWh/kg

A lower ratio can accompany a larger total

A lower ratio can accompany a larger totalThe invented periods change from 800 kWh/1000 kg to 900 kWh/1500 kg. The ratio falls 0.8 to 0.6 kWh/kg while the included electricity total increases. Original hypothetical comparison, not a physical energy-flow diagram. Arrows do not imply cause or a sustainability ranking; upstream and other outcomes need separate evidence.A: 800 kWh / 1000 kg0.8 kWh/kg within the statedservice boundaryB: 900 kWh / 1500 kg0.6 kWh/kg; equivalent deliveredfunction assumedIntensity falls 25%(0.8 − 0.6) / 0.8; a recordedratio changeTotal rises 12.5%100 kWh additional facilityelectricity0.8 kWh/kg0.6 kWh/kgcheck totalstoo
Original hypothetical comparison, not a physical energy-flow diagram. Arrows do not imply cause or a sustainability ranking; upstream and other outcomes need separate evidence.
Read the diagram as text

The invented periods change from 800 kWh/1000 kg to 900 kWh/1500 kg. The ratio falls 0.8 to 0.6 kWh/kg while the included electricity total increases.

Parts

A: 800 kWh / 1000 kg
0.8 kWh/kg within the stated service boundary
B: 900 kWh / 1500 kg
0.6 kWh/kg; equivalent delivered function assumed
Intensity falls 25%
(0.8 − 0.6) / 0.8; a recorded ratio change
Total rises 12.5%
100 kWh additional facility electricity

Connections

  • A: 800 kWh / 1000 kg → Intensity falls 25%: 0.8 kWh/kg
  • B: 900 kWh / 1500 kg → Intensity falls 25%: 0.6 kWh/kg
  • Intensity falls 25% → Total rises 12.5%: check totals too

Include outcomes that the ratio omits

Pair the resource record with questions about who can obtain the product, its price relative to people's means, and the labour and skills required. An average selling price cannot establish affordability for every household. More output does not demonstrate decent working conditions or equitable access.

Safety and product suitability also need appropriate process evidence. An absent verification record is not a measured zero failure rate. Avoid turning an unresolved safety question into a small negative score that can be cancelled by inexpensive electricity. Detailed hazard controls and their validation remain in the food-safety branch.

A score contains choices

Do not add kilograms, electricity, prices and survey percentages as though they were one physical quantity. A composite score requires a transformation and weighting rule. That rule expresses choices about which outcomes matter and how much compensation between them is allowed; it is not discovered merely by formatting a dashboard.

If a summary is useful, keep the underlying measures, weights, exclusions and data quality accessible. A missing value should remain identifiable, not become a favourable rating. Show important low-performing outcomes explicitly. Uncertainty about a measure and poor performance on that measure are different facts.

Let the evidence guide the next question

A small transparent display can state the measured result and its limit:'Electricity per delivered kilogram fell in these records, total facility demand rose, and upstream emissions and household affordability were not assessed.' It can then identify which missing evidence matters most for the decision.

Agree the reporting period and indicators before judging a change. Retain negative or unexpected findings and consult affected users and workers. Shared system and uncertainty Foundations support the reading; neighbouring topics develop resource accounts, evaluation design and food access. The dashboard should help readers examine evidence rather than force a predetermined winner.

Worked examples

Two electricity conclusions

How do the invented total and per-kilogram electricity records compare?

  1. Calculate 800/1000=0.8 kWh/kg and 900/1500=0.6 kWh/kg.
  2. Intensity falls by(0.8−0.6)/0.8×100=25%.
  3. Total rises by 900−800=100 kWh; 100/800×100=12.5%.

Recorded electricity intensity fell 25%, while included total electricity rose 12.5%. No complete impact or causal ranking follows.

Read a missing safety value

A summary assigns its best safety score because no verification result was entered. Is that justified?

  1. Distinguish missing evidence from an observed result.
  2. Identify the process-specific verification required for the claim.
  3. Display the gap rather than treating it as favourable performance.

No. An absent record does not establish safe output or a zero failure rate; the summary must retain that uncertainty.

Check your understanding

  1. Does lower facility electricity per kilogram establish lower total electricity?

    Show answer and reasoning

    No.

    The denominator can grow faster than total demand, as in the invented example.

  2. Can one price average establish affordability for all households?

    Show answer and reasoning

    No.

    Household resources, needs and access differ; the average omits their distribution.

  3. Should composite-score weights and exclusions be available to readers?

    Show answer and reasoning

    Yes.

    They affect the result and can hide important adverse outcomes.

Key ideas

  • Use the same useful function and an explicit boundary for comparison.
  • Read absolute resource totals beside ratios.
  • Keep access, livelihoods, safety evidence and environmental outcomes distinguishable.
  • Disclose summary rules, data quality and unresolved information.

References

Sources supporting the explanations and examples in this article.

  1. Food and Agriculture Organization of the United Nations2 sources
    1. Sustainability Assessment of Food and Agriculture Systems: Guidelines, version3.0Food and Agriculture Organization of the United NationsReference guide · PDFfao.orgRead source
    2. Sustainable Food Systems: Concept and FrameworkHanh NguyenReference guide · PDFfao.orgRead source