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Drawing No. EH–ES–012 // Environmental & Safety Engineering

Electricity Life-Cycle Assessment (LCA) Comparison Tool

Reviewed August 2026

Compare nuclear, coal, natural gas, hydropower, solar and wind across climate, water, health, ecosystem and resource indicators using a consistent UNECE life-cycle dataset.

Source UNECE 2021Full dataset Europe (EU28)Regional context 12 modeled regionsReference year 2020Method ILCD 2.0Functional unit 1 MWh delivered to grid

Read before comparing: these are scenario-specific, cradle-to-grave model results—not universal properties of a technology. Compare values only within this consistent dataset and indicator method.

What this electricity LCA comparison covers

One functional unit · one consistent method

Technologies compared

The model covers hard-coal and natural-gas generation with and without carbon capture, two hydropower scenarios, nuclear power, concentrated solar tower, ground-mounted polycrystalline-silicon and CdTe solar PV, and onshore and offshore wind.

More than carbon emissions

Results are expressed per 1 MWh delivered to the grid and separate 15 midpoint indicators for climate, air pollution, ecosystems, human health, dissipated water and resource use. The optional combined view remains preference-dependent and never replaces category-by-category interpretation.

Trade-off matrix

Each category is normalized independently

Cells show each result as a multiple of the lowest selected value in that category. Green means lower modeled impact within the current selection; it does not mean “impact-free.”

Preference-weighted screening index

Optional, transparent and value-dependent

Theme weights and included categories

Set theme importance with the sliders. Use the compact category controls to include or exclude individual indicators.

15 of 15 categories included

Relative combined profile

Included categories are normalized to fixed dataset medians and combined inside their themes before the visible theme weights are applied. Selecting a category in the main chart automatically includes it here.

Not an objective green score. A result of 1.00× matches the dataset's median environmental profile under the selected weights. Lower is better only within this dataset and these preferences; changing categories or weights can change the ranking. Weighting is an optional, value-dependent LCIA step [4].

Regional climate sensitivity

Europe point + matched 12-region technology range

Climate change · kg CO₂-eq/MWh

The dark marker is the exact European scenario used throughout the tool. The orange interval is UNECE's published minimum–maximum result across 12 modeled regions for the same technology configuration. The ranges distinguish CSP tower from trough, the two hydro cases, PV variants and offshore-wind foundations; they are regional context, not a second full LCA matrix.

12-region minimum–maximumEuropean scenario
Europe · full matrix15 indicatorsExact EU28 technology scenarios for 2020.
USA · coal-family context751 kg CO₂-eq/MWhIGCC endpoint; not used for the plotted hard-coal PC interval.
China · coal-family context1,095 kg CO₂-eq/MWhPulverized-coal endpoint reported in the study.

Category coverage audit

What the model includes—and what remains outside it

15

UNECE midpoint indicators included

Climate, air, nutrient enrichment, toxicity, radiation, water and resource-use categories from one method-consistent table.

1

Tabulated indicator deferred

Land use remains withheld because UNECE corrected the indicator after publication and a complete corrected technology matrix is not safely available for transcription.

Separate

Complementary assessments needed

Biodiversity, noise, visual effects, severe accidents, waste stewardship, grid integration, storage, reliability and local water scarcity are not reduced to these midpoint indicators.

Impact-category guide

Meaning, units and interpretation limits

Climate & air

Four indicators covering long-term climate forcing, stratospheric ozone, ground-level ozone formation and particulate-related health effects.

4 indicators

Climate change — total

kg CO₂-eq/MWh

Combines greenhouse gases according to their climate-change potential and includes fossil, biogenic and land-use-change contributions within the source model.

Interpret carefully: this is the full modeled life-cycle result, not only direct stack emissions and not a prediction of local climate effects.

Ozone layer depletion

mg CFC-11-eq/MWh

Expresses the potential of emitted substances to damage the stratospheric ozone layer relative to CFC-11.

Interpret carefully: this concerns the protective ozone layer high in the atmosphere; it is different from ground-level photochemical smog.

Photochemical ozone creation

kg NMVOC-eq/MWh

Represents the potential formation of ground-level ozone from precursor emissions such as nitrogen oxides and volatile organic compounds.

Interpret carefully: the indicator is an ozone-formation potential, not a measured concentration beside a specific plant.

Particulate-matter health effects

disease incidence/TWh

Models health effects associated with primary particulate emissions and secondary particles formed from precursor pollutants across the life cycle.

Interpret carefully: the result is a population-level characterization model output, not an observed count of illnesses caused by one facility.

Data: [1] · Indicator framework: [3]

Ecosystems & nutrients

Five indicators separating acidifying emissions, toxic effects in freshwater and three different nutrient-enrichment pathways.

5 indicators

Acidification

mol H⁺-eq/MWh

Converts acidifying emissions—principally sulphur, nitrogen and ammonia compounds—into an equivalent potential to release hydrogen ions.

Interpret carefully: it estimates potential pressure on soils and waters; it does not predict the pH at a particular site.

Freshwater ecotoxicity

CTUe/MWh

Combines modeled chemical fate, ecosystem exposure and toxic effect to compare potential harm to freshwater organisms.

Interpret carefully: CTUe is a comparative toxicity indicator with substantial inventory and model uncertainty, not a measured river concentration or ecological damage count.

Freshwater eutrophication

kg P-eq/MWh

Represents the potential for phosphorus-containing releases to enrich freshwater systems and stimulate excessive biological growth.

Interpret carefully: it is phosphorus-equivalent potential; marine and terrestrial nutrient effects are reported separately.

Marine eutrophication

kg N-eq/MWh

Represents the potential for nitrogen releases to contribute to nutrient enrichment and oxygen depletion in marine environments.

Interpret carefully: regional transport, nutrient limitation and receiving-water conditions strongly influence actual consequences.

Terrestrial eutrophication

mol N-eq/MWh

Measures potential ecosystem change caused by atmospheric deposition of reactive nitrogen compounds onto land.

Interpret carefully: this is not soil fertility or fertilizer value; excess nitrogen can alter species composition and ecosystem balance.

Data: [1] · Indicator framework: [3]

Human-health indicators

Three midpoint indicators covering modeled toxic effects and ionising-radiation impacts. They are not direct measurements of public exposure.

3 indicators

Carcinogenic human toxicity

CTUh/TWh

Combines modeled environmental fate, human exposure and carcinogenic effect factors for toxic substances released during the life cycle.

Interpret carefully: use it for comparative screening within the same method. It is not a site-specific risk assessment or an observed cancer count.

Non-carcinogenic human toxicity

CTUh/TWh

Applies the same fate–exposure–effect framework to potential non-cancer health effects from toxic releases.

Interpret carefully: toxicity results can be sensitive to incomplete inventories and characterization factors; small differences should not be overinterpreted.

Ionising radiation — human health

kg U-235-eq/MWh

Characterizes potential human-health effects from routine life-cycle radionuclide emissions using the ILCD U-235-equivalent reference.

Interpret carefully: it is not sieverts, individual dose, accident risk, radioactive-waste quantity or kilograms of U-235 released.

Data: [1] · Indicator framework: [3]

Water

The source reports dissipated water. This is only one water dimension and must not be confused with abstraction or local scarcity.

1 indicator

Dissipated water

m³/MWh

Counts water made unavailable to the immediate environment, including evaporation or incorporation into products, across the modeled life cycle.

Interpret carefully: it is not gross withdrawal, discharge volume, water quality or scarcity-weighted consumption. A site-specific water assessment is still required.

Data and definition: UNECE Table 13 and Section 4.6 [1]

Resources

Two indicators describing cumulative non-renewable primary-energy demand and modeled depletion pressure for minerals and metals.

2 indicators

Non-renewable energy demand — CED

GJ/MWh

Totals non-renewable primary energy required throughout the life cycle, rather than only electricity consumed at the generating plant.

Interpret carefully: UNECE notes that the applied method groups uranium under “fossil,” although uranium is not a fossil fuel. The value is therefore labelled non-renewable energy demand here.

Minerals and metals resource use

mg Sb-eq/MWh

Converts the modeled depletion pressure associated with mineral and metal extraction into antimony-equivalent units.

Interpret carefully: this is not material mass, supply-chain criticality, recyclability, mine toxicity or geopolitical risk; those require separate indicators.

Data: [1] · Indicator framework: [3]

Important missing dimension: land use is not shown because UNECE corrected the published indicator and a complete corrected technology table is not available for reliable transcription. Biodiversity, landscape fragmentation and ecosystem quality also cannot be inferred from land area alone.

How to interpret the comparison

Boundaries matter as much as numbers

What is included

Construction, fuel supply where applicable, operation and end-of-life processes in the UNECE technology scenarios, expressed per unit of electricity delivered to the grid.

What is not included

Additional transmission connections, system balancing, storage, catastrophic failures and several non-LCIA concerns such as noise, aesthetics, waste stewardship and some biodiversity effects.

Do not read ionising radiation as dose

The unit kg U-235 equivalent is an ILCD environmental characterization result. It is not sieverts, individual risk, actual U-235 released or an accident indicator.

Do not read dissipated water as withdrawal

UNECE counts water made unavailable to the immediate environment, such as evaporation. Water withdrawn and promptly returned is excluded; project-specific cooling performance can still differ.

One energy-method quirk matters

The source warns that its cumulative-energy-demand method groups uranium under “fossil,” although uranium is not a fossil fuel. The tool therefore labels this category non-renewable energy demand.

Methodology, limitations and sources

Transparent by design

Data and conversions

Fifteen impact values are transcribed from UNECE Table 14, except dissipated water, which uses the explicit two-significant-figure results in Table 13. This is intentional: Table 13 agrees with Section 4.6 and the report conclusions, while the Table 14 water column is inconsistent with them. Values originally stated per kWh are converted to the displayed per-MWh or per-TWh units by powers of ten only. The two hydro scenarios remain separate because reservoir emissions and site conditions can dominate results.

Regional coverage

The complete indicator matrix represents European scenarios. UNECE also modeled 12 world regions, but it publishes many regional results only in figures. The regional panel therefore uses the report's configuration-specific climate minimum–maximum ranges and keeps the exact Europe values as separate points. This distinction matters: the 27–122 kg CO₂-eq/MWh range is for CSP trough, while the tower scenario used here has a 14–87 kg CO₂-eq/MWh range. The named USA and China coal endpoints use different configurations and must not be read as a controlled country-only comparison.

Combined screening method

The optional index first divides every included indicator by its median across the complete 12-technology dataset. It calculates a geometric mean of the included categories inside each of five themes, then applies the visible theme weights through a second weighted geometric mean. All 15 categories and equal theme weights are the default; individual categories or whole themes can be excluded. This prevents categories with large numerical units, or themes containing more indicators, from dominating automatically. It does not remove the subjective judgement introduced by selecting categories, themes and weights.

Important limitations

The source models European scenarios representative of 2020. Results depend on capacity factor, lifetime, fuel supply, manufacturing electricity, geography and other assumptions. They should not be used as a procurement-grade LCA or transferred to a specific project without adjustment. Land use is withheld from this release pending a complete corrected technology table. Toxicity indicators have high model uncertainty and should be interpreted as comparative screening results.

Primary sources and standards

UNECE — Life Cycle Assessment of Electricity Generation Options (March 2022 edition)UNECE — corrigendum (July 2022)European Commission JRC — weighting for Environmental FootprintISO 14040 — LCA principles and frameworkISO 14044 — LCA requirements and guidelinesEuropean Commission — Environmental Footprint methods

References and data provenance

Primary and official sources first

Model elementMaterial usedHow it is used
Fourteen impact indicatorsUNECE electricity LCA [1]European 2020 scenario values transcribed from Table 14 and converted from per-kWh to the displayed units.
Dissipated waterUNECE electricity LCA [1]Table 13 values, checked against Section 4.6 and the report conclusions, replace the internally inconsistent water column in Table 14.
Regional climate contextUNECE electricity LCA [1]Configuration-matched minimum–maximum climate ranges across 12 modeled regions. CSP tower uses 14–87; the 27–122 range belongs to CSP trough.
Land-use exclusionUNECE corrigendum [2]The corrected indicator is acknowledged but withheld because a complete corrected technology matrix is not available for reliable transcription.
Indicator names, units and interpretationUNECE [1] and ILCD recommendations [3]Defines the midpoint categories and reference units used in the selector, chart and category guide.
Combined screening indexJRC weighting report [4]Supports the disclosure that normalization and weighting are optional and inherently value-dependent. EngineerHub's geometric aggregation remains its own transparent screening implementation.
LCA structure and limitationsISO 14040 [5], ISO 14044 [6] and EU Environmental Footprint recommendation [7]Supports the goal-and-scope, inventory, impact-assessment and interpretation framework and the need to disclose methods and boundaries.
[1] United Nations Economic Commission for Europe — Life Cycle Assessment of Electricity Generation Options. 2021 report, March 2022 edition. Direct numerical basis for the European matrix and regional ranges. Source page ↗
[2] UNECE — Corrigendum to the Life Cycle Assessment of Electricity Generation Options. July 2022. Used to identify the corrected land-use issue. Corrigendum ↗
[3] European Commission, Joint Research Centre — ILCD Handbook: Recommendations for Life Cycle Impact Assessment in the European Context. EUR 24571 EN, 2011. Used for category definitions, characterization concepts and units. Report ↗
[4] Sala, S. et al., European Commission JRC — Development of a Weighting Approach for the Environmental Footprint. 2018. Used for the normalization and weighting limitations. Report ↗
[5] International Organization for Standardization — ISO 14040:2006. Environmental management: life cycle assessment, principles and framework. Standard page ↗
[6] International Organization for Standardization — ISO 14044:2006. Environmental management: life cycle assessment, requirements and guidelines. Standard page ↗
[7] European Commission — Commission Recommendation (EU) 2021/2279. Recommendation on the use of Environmental Footprint methods. Official text ↗

Frequently asked questions

Six common interpretation traps

What is life-cycle assessment for electricity?

Life-cycle assessment estimates environmental impacts across construction, fuel supply, operation and end-of-life stages for a common functional unit.

Can different LCA categories be combined?

Only after normalization and weighting, which introduce value judgements. The optional screening index makes both steps explicit, groups the indicators into balanced themes and remains separate from the primary category-by-category comparison. It is not an objective environmental score.

Does the tool contain complete results for multiple regions?

No. The complete indicator matrix is the European scenario. The regional panel uses UNECE's published climate ranges across 12 modeled regions and does not invent full regional datasets where numerical tables are unavailable.

Are all important environmental categories included?

The tool includes 15 of the 16 distinct midpoint indicators tabulated by UNECE. Land use is deferred because the source corrected that indicator. Biodiversity, noise, severe accidents, waste stewardship, grid integration and local water scarcity still need separate assessment.

Is kg U-235 equivalent a radiation dose?

No. It is an environmental impact characterisation unit used by the ILCD method, not a dose to a person and not a mass of U-235 released.

Is dissipated water the same as water withdrawal?

No. Dissipated water is water made unavailable to the immediate environment, for example through evaporation or incorporation into products. Water withdrawn and promptly returned is excluded.

Electricity LCA learning guides

Understand the evidence behind the tool

Related EngineerHub tools

Continue the analysis

Reviewed 27 August 2026 against UNECE Tables 13 and 14 · Dataset version: UNECE 2021 / correction checked 2022