Application-led decision support

Which PV technology suits your application?

Choose an application and the outcomes that matter most. The selector ranks PV technology families and explains their benefits and trade-offs without directing you to a particular manufacturer or model.

Method and limitations About the guidance Open methodology

The ranking uses transparent, comparative scores for nine criteria: affordability, conversion efficiency, area efficiency, service life, heat tolerance, low-light performance, form-factor flexibility, resource and circularity considerations, and lifecycle climate impact. Scores describe broad technology families rather than individual products.

The four-part location globe is a broad latitude screening input. The northern and southern high-latitude bands increase the influence of low-light behaviour, service life, and area use; the two bands adjoining the equator increase the influence of heat performance and service life. Heat and low-light performance are inferred from this location choice and are therefore not separate priority controls. Hemisphere by itself does not determine local climate, so this adjustment must not be treated as a site-energy calculation.

The resource and circularity score considers material availability, critical or hazardous material exposure, service life, and current recovery pathways. It is deliberately qualitative because harmonised life-cycle inventories are unavailable for every technology family. It must not be read as proof that the overall top-ranked technology has the lowest environmental impact.

Final selection should also consider site irradiation, shading, structural loads, fire and electrical requirements, warranties, supply-chain availability, installer capability, and a project-specific financial assessment.

Authoritative inputs for a project-grade calculation

The sources below can replace broad family assumptions with traceable product and site inputs. Laboratory records remain useful for technology potential, but commercial-module and field evidence should control a project recommendation.

Location and annual energy yield

Inputs: irradiance, diffuse fraction, temperature, wind, horizon, mounting position, orientation, and technology-specific performance coefficients.

Sources: European Commission PVGIS, the Sandia PVPMC modelling guide, and IEA PVPS climatic rating.

Calculation use: compare annual delivered energy and energy per available area for the actual site instead of relying on standard-test efficiency alone.

Reliability and service life

Inputs: qualification status, field degradation, failure modes, warranty terms, climate stressors, and evidence duration.

Sources: IEC 61215-1, IEA PVPS service-life estimation, and its new-technology failure review.

Calculation use: model year-by-year energy and uncertainty. Passing IEC qualification is an eligibility check, not a numerical lifetime prediction.

Application, safety, and physical fit

Inputs: module mass and dimensions, mechanical loads, fire and electrical classification, flexibility, mounting restrictions, and application-specific stressors.

Sources: product certificates and datasheets, IEC 61730-1, IEC TS 63126 for high-temperature operation, IEC TS 63163 for portable products, and IEA PVPS application guidance.

Calculation use: apply pass/fail constraints before ranking, then compare only products suitable for the roof, façade, portable system, or ground-mounted site.

Cost and lifetime value

Inputs: current module quote, balance-of-system cost, installation cost, replacement risk, maintenance, annual energy, and degradation.

Sources: current supplier and installer quotations, with the NREL technology-cost benchmark retained only as a dated fallback for family-level screening.

Calculation use: compare lifetime cost of delivered electricity and total project cost rather than module price alone.

Environment, materials, and circularity

Inputs: verified product declarations, lifecycle greenhouse-gas emissions, manufacturing location and electricity mix, material inventory, repairability, collection, and recovery route.

Sources: IEA PVPS lifecycle assessment, its module-recycling review, and NREL PV ICE.

Calculation use: compare equivalent functional units and system boundaries; report climate, resource, toxicity, and circularity indicators separately.

Recommended calculation sequence

  1. Eligibility: remove products that fail application, safety, structural, electrical, availability, or certification requirements.
  2. Site yield: combine location weather with product performance coefficients to estimate annual energy and energy per available area.
  3. Lifetime: apply evidence-based degradation and failure scenarios to estimate lifetime delivered energy.
  4. Cost: divide project lifecycle cost by lifetime energy and retain the underlying capital and replacement costs.
  5. Environmental performance: compare verified lifecycle indicators using the same boundary, location, lifetime, and functional unit.
  6. Decision and uncertainty: weight the project priorities, show missing inputs separately, and test whether reasonable changes alter the leading option.

Evidence rule: product-specific measured data should take precedence over technology-family averages. Research-cell records should indicate future potential only, and emerging technologies should remain clearly labelled until large-area module, durability, manufacturing, and bankability evidence is available.

Best fit for your selections

Technology recommendation

PV technology trade-off spider diagram Relative scores for the selected PV technology. Higher values represent more favourable performance.

How to read the chart

Scores are relative, from 0 to 100. Farther from the centre is more favourable. A higher cost score means greater affordability, and a higher area score means less area is needed.

Selected technology scores

Benefits

    Trade-offs

      Ranked alternatives

      Compare another technology

      Resource and circularity basis

      This is a qualitative screening score, not a product environmental declaration or a comparative life-cycle assessment. Results change with manufacturing location, electricity mix, module design, lifetime, yield, and end-of-life route.

      Transparent scoring

      How this recommendation is calculated

      Normalised value100 × position between fixed lower and upper anchors

      Graph score50 + evidence factor × (normalised value − 50)

      Fit scoreΣ(graph score × application weight) ÷ Σ(application weights)

      Evidence factors are 1.00 for high confidence, 0.75 for medium confidence, and 0.35 for low confidence. Low-confidence estimates are pulled towards the neutral score of 50 instead of being allowed to create an unsupported extreme. The environmental-friendliness axis currently uses inverse lifecycle greenhouse-gas intensity. It measures climate impact only; toxicity, water, land, biodiversity, and other environmental effects require additional harmonised indicators. A project-grade comparison should replace every low-confidence proxy with site-specific yield data, supplier quotations, product datasheets, warranties, and verified environmental product declarations.