Benchmark WI-VAL · version 1.1.0 · released 2026-08-01

Where the model is right, and where it is wrong

A model that is never checked against reality is an opinion with equations. WI-SL v1.2.0 is run blind against published field trials, standardised durability tests and in-service inspections, and every residual is published — including the ones that embarrass us.

Read the method

Headline

Aggregate accuracy across the benchmark

Cases
24
External observations
Bias
-0.5 yr
Model runs conservative
MAE
8.5 yr
Mean absolute error
RMSE
11.2 yr
Penalises large misses
Coverage
87.5%
Inside P10–P90 · target 80%
r
0.63
Predicted vs observed

Coverage is the honest number to watch. If far fewer than 80% of observations land inside the modelled P10–P90 band, the declared uncertainty is too narrow and the intervals are overconfident. If far more, the model is hedging and the bands carry little information. The widest single miss in this release is European Oak · Stockholm, Sweden at -22.5 years.

Current status, stated plainly: the headline row above is in-sample — the WI-CAL correction was fitted on these same cases, so it flatters the model by construction. The number to judge us by is the blind leave-one-out row below, where each case is predicted with the calibration refitted without it. Specify against the P10, not the P50.

Calibration WI-CAL v1.1.0

What the correction changed, and what it cost

Model stateBias (yr)MAE (yr)RMSE (yr)MAPECoverager
Uncalibrated (WI-SL 1.1.0 physics only)+19.622.326.5121.4%0%0.36
Blind — leave-one-out calibration09.512.637.5%83.3%0.56
In-sample calibrated (WI-SL 1.2.0)-0.58.511.233.1%87.5%0.63
Estimator
log-space mean
log-space mean residual, shrunk to the global factor
Global factor
×0.547
Applied where a zone is unfitted
Zone factors
A 0.3268 · B 0.441 · C 0.7014 · D 0.6906 · E 0.547
Shrunk with 2 pseudo-observations
σ inflation
×4.5
Residual spread needed to reach 80% coverage

Two honest readings of this table. First: the physics-only model was optimistic by a factor of roughly 1.8, and a flat multiplicative correction removes almost all of that bias without touching a single equation — so the error was in the level, not the ranking. Second: reaching real 80% interval coverage required inflating the residual σ by ×4.5. The declared input uncertainties alone understated true scatter roughly fourfold. Wide bands are the truth here; narrow ones were fiction.

Service life only. Maintenance interval, silvering and performance score are uncalibrated. Correlation (r) stays modest, which is the remaining open problem: the correction fixes the average, not the case-by-case ordering. That needs more field records, not more maths.

By climate zone

Accuracy is not uniform across the planet

Köppen zonenBiasMAERMSEMAPECoverage
A — tropical4+2.63.54.737.1%75%
B — arid5+0.93.85.421.5%100%
C — temperate9-0.612.113.441.7%88.9%
D — continental6-3.610.51427%83.3%

Zones with one or two cases are reported for transparency, not for confidence. Treat any row with n < 4 as anecdote. The tropical and arid rows are where the method most needs field data — if you hold inspection records from those zones, we want them.

By species

Where the species parameters, not the climate, are wrong

SpeciesnBiasMAERMSEMAPECoverage
Thermally Modified Ash5+151515.772.5%100%
European Oak3-8.18.11315.6%100%
Siberian Larch4-6.78.411.230.9%75%
Norway Spruce4-6.47.510.133.9%50%
Acetylated Radiata Pine4-2.92.93.68.2%100%
Western Red Cedar4+0.27.68.923.1%100%

The calibration layer corrects by climate zone only, so any bias left in this table is a species-parameter problem: a resistance value, a modification credit or a coating assumption that does not hold. Rows are sorted by absolute bias, worst first. We publish this before we fix it, because the ordering tells a specifier which of our numbers to distrust today.

Case by case

Every observation, every residual

  1. val-01 · field trial

    Norway SpruceUppsala / central Sweden, above-ground field station

    Mapped to Stockholm, Sweden (Dfb — humid continental) · south · sheltered · untreated

    inside P10–P90
    Observed
    12 yr
    source range 9–16 yr
    Modelled P50
    13.3 yr
    P10–P90 5–23.5 yr
    Blind (LOO)
    13.4 yr
    uncalibrated 19.2 yr · zone factor ×0.6906
    Residual
    +1.3 yr
    +10.8% of observed
    Observation ran
    10 yr
    source extrapolated beyond exposure

    Untreated spruce cladding, ventilated cavity, no coating. Failure criterion: onset of decay rating 2 on the EN 252 scale.

    Source (institute report): EN 252 / above-ground double-layer field testing, Nordic stationsRISE / Nordic Wood Preservation Council field test summaries for untreated Picea abies, above-ground exposure

  2. val-02 · in service survey

    Siberian LarchStockholm archipelago, unpainted larch façade

    Mapped to Stockholm, Sweden (Dfb — humid continental) · south · fully exposed · untreated

    outside P10–P90
    Observed
    42 yr
    source range 35–55 yr
    Modelled P50
    22.5 yr
    P10–P90 7–40.7 yr
    Blind (LOO)
    19.6 yr
    uncalibrated 32.4 yr · zone factor ×0.6906
    Residual
    -19.5 yr
    -46.4% of observed
    Observation ran
    40 yr
    source extrapolated beyond exposure

    Heartwood-selected boards, 25 mm cavity. Silvered within 2 years; replacement driven by board cupping, not decay.

    Source (institute report): Nordic in-service façade inspections, untreated Larix sibiricaDocumented Swedish/Finnish façade inspection surveys of unpainted Siberian larch cladding

  3. val-03 · in service survey

    Western Red CedarVancouver region, coastal Pacific North-West

    Mapped to Pacific North-West, USA (Csb — warm-summer mediterranean) · north · sheltered · untreated

    inside P10–P90
    Observed
    45 yr
    source range 30–60 yr
    Modelled P50
    33.3 yr
    P10–P90 10–60.7 yr
    Blind (LOO)
    33 yr
    uncalibrated 48.6 yr · zone factor ×0.7014
    Residual
    -11.7 yr
    -26% of observed
    Observation ran
    45 yr
    full observation period

    Vertical grain heartwood. Long life in its native climate; sapwood-rich boards perform markedly worse.

    Source (institute report): Western red cedar in-service performance, coastal British ColumbiaFPInnovations / regional building-envelope surveys of Thuja plicata cladding

  4. val-04 · field trial

    Thermally Modified AshNorth-west European maritime coast, thermally modified hardwood cladding

    Mapped to Coastal Scotland (Cfb — temperate oceanic) · east-west · fully exposed · untreated

    inside P10–P90
    Observed
    27 yr
    source range 20–35 yr
    Modelled P50
    45 yr
    P10–P90 11.2–80 yr
    Blind (LOO)
    45.7 yr
    uncalibrated 65.2 yr · zone factor ×0.7014
    Residual
    +18 yr
    +66.7% of observed
    Observation ran
    12 yr
    source extrapolated beyond exposure

    Source extrapolates from 12 years of exposure. Extrapolated observations carry more weight of assumption than the model does.

    Source (peer reviewed): Thermally modified timber above-ground durability trialsAbove-ground field trials of thermally modified hardwoods (Thermowood class D), maritime temperate exposure

  5. val-05 · in service survey

    European OakScottish east coast, untreated oak boarding

    Mapped to Coastal Scotland (Cfb — temperate oceanic) · south · fully exposed · untreated

    inside P10–P90
    Observed
    35 yr
    source range 25–50 yr
    Modelled P50
    33.7 yr
    P10–P90 10.4–59.7 yr
    Blind (LOO)
    34 yr
    uncalibrated 48.3 yr · zone factor ×0.7014
    Residual
    -1.3 yr
    -3.7% of observed
    Observation ran
    35 yr
    full observation period

    Heartwood only. Tannin run-off staining is a serviceability issue long before decay is.

    Source (institute report): European oak cladding, UK maritime in-service recordsTRADA / BRE durability guidance and inspection records for Quercus robur external boarding

  6. val-06 · standardised test

    Acetylated Radiata PineNetherlands / UK coastal, acetylated radiata pine

    Mapped to Coastal Scotland (Cfb — temperate oceanic) · east-west · fully exposed · untreated

    inside P10–P90
    Observed
    50 yr
    source range 40–60 yr
    Modelled P50
    44.1 yr
    P10–P90 13.4–80 yr
    Blind (LOO)
    45.8 yr
    uncalibrated 67.8 yr · zone factor ×0.7014
    Residual
    -5.9 yr
    -11.8% of observed
    Observation ran
    20 yr
    source extrapolated beyond exposure

    Manufacturer-independent trials confirm class 1 durability; the 50-year figure is a warranty-anchored expectation, not a completed observation.

    Source (peer reviewed): Acetylated wood above-ground durability, EN 350 durability class 1 assessmentField and laboratory durability assessments of acetylated Pinus radiata, above-ground use class 3

  7. val-07 · service life database

    Norway SpruceUK maritime, painted spruce cladding with maintained coating

    Mapped to Coastal Scotland (Cfb — temperate oceanic) · north · sheltered · maintained coating

    outside P10–P90
    Observed
    30 yr
    source range 20–40 yr
    Modelled P50
    13.1 yr
    P10–P90 5–23.9 yr
    Blind (LOO)
    12 yr
    uncalibrated 19.6 yr · zone factor ×0.7014
    Residual
    -16.9 yr
    -56.3% of observed
    Observation ran
    30 yr
    full observation period

    Conditional on a maintained coating system. Without recoating at interval, observed life collapses toward the untreated case.

    Source (database): Component service-life data for maintained painted softwood claddingISO 15686-8 factor-method reference service lives for coated softwood external cladding

  8. val-08 · field trial

    Siberian LarchEquatorial South-East Asia, temperate softwood in tropical exposure

    Mapped to Singapore (Af — tropical rainforest) · south · fully exposed · untreated

    inside P10–P90
    Observed
    7 yr
    source range 4–11 yr
    Modelled P50
    9.4 yr
    P10–P90 5–17.1 yr
    Blind (LOO)
    10.1 yr
    uncalibrated 30 yr · zone factor ×0.3268
    Residual
    +2.4 yr
    +34.3% of observed
    Observation ran
    6 yr
    source extrapolated beyond exposure

    The hardest case for the model. Tropical bio-load dominates and station density is poor — the zone σ multiplier is 1.45 for a reason.

    Source (peer reviewed): Tropical above-ground decay hazard trials, imported temperate speciesTropical field trials showing 5–10× decay-rate acceleration versus temperate stations for the same species

  9. val-09 · in service survey

    European OakArabian interior, shaded hardwood screening

    Mapped to Riyadh, Saudi Arabia (BWh — hot desert) · south · fully exposed · untreated

    inside P10–P90
    Observed
    18 yr
    source range 12–25 yr
    Modelled P50
    17.6 yr
    P10–P90 5.7–31.3 yr
    Blind (LOO)
    18.1 yr
    uncalibrated 41.8 yr · zone factor ×0.441
    Residual
    -0.4 yr
    -2.2% of observed
    Observation ran
    15 yr
    source extrapolated beyond exposure

    Decay is near-absent; failure is UV, checking and thermal movement. The model's decay-led framing under-predicts this failure mode.

    Source (institute report): Hot-arid exterior timber inspections, Gulf regionGulf-region building-envelope inspections of exterior hardwood screens and shading elements

  10. val-10 · in service survey

    Acetylated Radiata PineGulf coastal, acetylated pine louvres

    Mapped to Dubai, UAE (BWh — hot desert, coastal) · east-west · fully exposed · untreated

    inside P10–P90
    Observed
    30 yr
    source range 22–40 yr
    Modelled P50
    26.3 yr
    P10–P90 8.1–47.8 yr
    Blind (LOO)
    25.3 yr
    uncalibrated 61.2 yr · zone factor ×0.441
    Residual
    -3.7 yr
    -12.3% of observed
    Observation ran
    12 yr
    source extrapolated beyond exposure

    Stainless fixings throughout. Where galvanised fixings were used, elements failed at the fastener 10–15 years earlier.

    Source (institute report): Coastal Gulf in-service inspections of modified wood elementsDocumented inspections of acetylated softwood louvres and decking in chloride-laden coastal exposure

  11. val-11 · in service survey

    Western Red CedarSouthern Scandinavia, imported cedar cladding

    Mapped to Stockholm, Sweden (Dfb — humid continental) · south · sheltered · untreated

    inside P10–P90
    Observed
    33 yr
    source range 25–45 yr
    Modelled P50
    35.7 yr
    P10–P90 11.1–65.5 yr
    Blind (LOO)
    35.4 yr
    uncalibrated 52.1 yr · zone factor ×0.6906
    Residual
    +2.7 yr
    +8.2% of observed
    Observation ran
    30 yr
    source extrapolated beyond exposure

    Performs below its native-climate life; extractive leaching under higher driving rain shortens the plateau.

    Source (institute report): Imported Thuja plicata cladding, Scandinavian inspection recordsScandinavian façade inspections of imported western red cedar, ventilated rainscreen build-ups

  12. val-12 · field trial

    Thermally Modified AshCoastal Oregon, modified hardwood rainscreen

    Mapped to Pacific North-West, USA (Csb — warm-summer mediterranean) · east-west · fully exposed · untreated

    inside P10–P90
    Observed
    24 yr
    source range 18–32 yr
    Modelled P50
    44.7 yr
    P10–P90 13–80 yr
    Blind (LOO)
    50.1 yr
    uncalibrated 68.1 yr · zone factor ×0.7014
    Residual
    +20.7 yr
    +86.3% of observed
    Observation ran
    10 yr
    source extrapolated beyond exposure

    Modification reduces decay but not surface checking; the model tracks the first and only partly the second.

    Source (peer reviewed): North American above-ground trials of thermally modified hardwoodAbove-ground stake and cladding trials of thermally modified hardwoods, wet-temperate exposure

  13. val-13 · field trial

    Norway SpruceEquatorial South-East Asia, untreated temperate softwood

    Mapped to Singapore (Af — tropical rainforest) · north · sheltered · untreated

    outside P10–P90
    Observed
    4 yr
    source range 2–6 yr
    Modelled P50
    5 yr
    P10–P90 5–8.3 yr
    Blind (LOO)
    5 yr
    uncalibrated 14.1 yr · zone factor ×0.3268
    Residual
    +1 yr
    +25% of observed
    Observation ran
    5 yr
    full observation period

    Termite attack co-occurs with fungal decay; the model treats bio-load as a single term and cannot separate the two.

    Source (peer reviewed): Tropical above-ground decay hazard trials, non-durable softwoodsAbove-ground tropical field trials of non-durable softwood, EN 252 / use class 3 equivalents

  14. val-14 · in service survey

    Acetylated Radiata PineSingapore, acetylated pine louvres and screens

    Mapped to Singapore (Af — tropical rainforest) · east-west · fully exposed · untreated

    inside P10–P90
    Observed
    22 yr
    source range 15–30 yr
    Modelled P50
    20.2 yr
    P10–P90 6.1–36.4 yr
    Blind (LOO)
    20.8 yr
    uncalibrated 63.7 yr · zone factor ×0.3268
    Residual
    -1.8 yr
    -8.2% of observed
    Observation ran
    11 yr
    source extrapolated beyond exposure

    Still short of the observation window it claims; the upper bound is a projection from 11 years of service.

    Source (institute report): Tropical in-service inspections of acetylated softwoodDocumented South-East Asian inspections of acetylated Pinus radiata external elements

  15. val-15 · field trial

    Thermally Modified AshTropical rainscreen, thermally modified hardwood

    Mapped to Singapore (Af — tropical rainforest) · south · fully exposed · untreated

    inside P10–P90
    Observed
    11 yr
    source range 7–16 yr
    Modelled P50
    19.9 yr
    P10–P90 5.6–35.3 yr
    Blind (LOO)
    22.9 yr
    uncalibrated 61.8 yr · zone factor ×0.3268
    Residual
    +8.9 yr
    +80.9% of observed
    Observation ran
    8 yr
    source extrapolated beyond exposure

    Thermal modification loses much of its relative advantage where wetting is near-continuous.

    Source (peer reviewed): Thermally modified hardwood in tropical above-ground exposureComparative above-ground trials of thermally modified hardwoods, humid tropical stations

  16. val-16 · in service survey

    Western Red CedarArabian interior, cedar soffits under deep shading

    Mapped to Riyadh, Saudi Arabia (BWh — hot desert) · north · sheltered · untreated

    inside P10–P90
    Observed
    26 yr
    source range 18–35 yr
    Modelled P50
    22.8 yr
    P10–P90 5.6–40.2 yr
    Blind (LOO)
    22.4 yr
    uncalibrated 52.3 yr · zone factor ×0.441
    Residual
    -3.2 yr
    -12.3% of observed
    Observation ran
    20 yr
    source extrapolated beyond exposure

    Shading removes the dominant UV term; remaining failure is dimensional movement at fixings.

    Source (institute report): Hot-arid in-service inspections of softwood soffitsGulf-region envelope inspections of shaded softwood soffits and ceilings

  17. val-17 · in service survey

    Thermally Modified AshGulf coastal, modified hardwood screens

    Mapped to Dubai, UAE (BWh — hot desert, coastal) · south · fully exposed · untreated

    inside P10–P90
    Observed
    15 yr
    source range 10–22 yr
    Modelled P50
    26 yr
    P10–P90 7.8–46.9 yr
    Blind (LOO)
    27.6 yr
    uncalibrated 58.5 yr · zone factor ×0.441
    Residual
    +11 yr
    +73.3% of observed
    Observation ran
    12 yr
    source extrapolated beyond exposure

    Abrasive dust accelerates surface loss; the model has no abrasion term and over-predicts here.

    Source (institute report): Coastal Gulf inspections of thermally modified hardwoodInspection records of thermally modified hardwood screens in chloride and dust-laden exposure

  18. val-18 · in service survey

    Siberian LarchGulf coastal, untreated larch decking and screens

    Mapped to Dubai, UAE (BWh — hot desert, coastal) · east-west · fully exposed · untreated

    inside P10–P90
    Observed
    12 yr
    source range 8–18 yr
    Modelled P50
    12.9 yr
    P10–P90 5–23.4 yr
    Blind (LOO)
    12.7 yr
    uncalibrated 29.8 yr · zone factor ×0.441
    Residual
    +0.9 yr
    +7.5% of observed
    Observation ran
    12 yr
    full observation period

    Failure is checking and cupping under thermal cycling long before any decay is measurable.

    Source (institute report): Temperate softwood in hot-arid coastal serviceGulf-region inspections of imported Larix sibirica external elements

  19. val-19 · in service survey

    European OakCentral Sweden, untreated oak boarding and structure

    Mapped to Stockholm, Sweden (Dfb — humid continental) · east-west · fully exposed · untreated

    inside P10–P90
    Observed
    55 yr
    source range 40–80 yr
    Modelled P50
    32.5 yr
    P10–P90 9.9–58.6 yr
    Blind (LOO)
    30.6 yr
    uncalibrated 48.5 yr · zone factor ×0.6906
    Residual
    -22.5 yr
    -40.9% of observed
    Observation ran
    55 yr
    full observation period

    Heartwood only, with ventilated backs and no ground contact. Sapwood-bearing boards fail decades earlier.

    Source (institute report): Nordic in-service records for Quercus robur heartwood exteriorSwedish inspection records of untreated oak boarding and exposed oak structure

  20. val-20 · service life database

    Norway SpruceCoastal Oregon / Washington, painted spruce cladding

    Mapped to Pacific North-West, USA (Csb — warm-summer mediterranean) · north · sheltered · maintained coating

    inside P10–P90
    Observed
    25 yr
    source range 18–35 yr
    Modelled P50
    14.1 yr
    P10–P90 5–25.5 yr
    Blind (LOO)
    12.9 yr
    uncalibrated 19.9 yr · zone factor ×0.7014
    Residual
    -10.9 yr
    -43.6% of observed
    Observation ran
    25 yr
    full observation period

    Conditional on recoating at interval; the database value assumes maintenance is actually carried out.

    Source (database): Component service-life data for coated softwood in wet-temperate exposureISO 15686-8 factor-method reference service lives, coated softwood cladding, high driving-rain regions

  21. val-21 · in service survey

    Siberian LarchScottish west coast, unpainted larch rainscreen

    Mapped to Coastal Scotland (Cfb — temperate oceanic) · north · fully exposed · untreated

    inside P10–P90
    Observed
    30 yr
    source range 22–40 yr
    Modelled P50
    19.4 yr
    P10–P90 7.1–35.4 yr
    Blind (LOO)
    19.4 yr
    uncalibrated 29 yr · zone factor ×0.7014
    Residual
    -10.6 yr
    -35.3% of observed
    Observation ran
    28 yr
    source extrapolated beyond exposure

    Algal colonisation within two years on north elevations; a serviceability, not a structural, limit.

    Source (institute report): UK maritime in-service inspections of untreated larchTRADA / UK envelope inspection records for Larix cladding in high driving-rain exposure

  22. val-22 · in service survey

    Western Red CedarUK maritime, imported cedar cladding with translucent coating

    Mapped to Coastal Scotland (Cfb — temperate oceanic) · south · fully exposed · maintained coating

    inside P10–P90
    Observed
    28 yr
    source range 20–38 yr
    Modelled P50
    40.8 yr
    P10–P90 11.9–71.9 yr
    Blind (LOO)
    43.5 yr
    uncalibrated 59.5 yr · zone factor ×0.7014
    Residual
    +12.8 yr
    +45.7% of observed
    Observation ran
    26 yr
    source extrapolated beyond exposure

    Coating failure at 6–9 year intervals drives the maintenance cost long before the substrate is at risk.

    Source (institute report): Coated Thuja plicata cladding, UK maritime inspection recordsUK inspection records of translucent-coated western red cedar rainscreens

  23. val-23 · service life database

    Acetylated Radiata PineNordic continental, acetylated pine windows and cladding

    Mapped to Stockholm, Sweden (Dfb — humid continental) · south · fully exposed · untreated

    inside P10–P90
    Observed
    45 yr
    source range 35–60 yr
    Modelled P50
    44.8 yr
    P10–P90 13.9–80 yr
    Blind (LOO)
    46.3 yr
    uncalibrated 66.3 yr · zone factor ×0.6906
    Residual
    -0.2 yr
    -0.4% of observed
    Observation ran
    18 yr
    source extrapolated beyond exposure

    Warranty-anchored again. 18 years of real service; the remainder is projection and is flagged as such.

    Source (database): Nordic service-life records for acetylated softwood joineryComponent service-life records for acetylated Pinus radiata joinery and cladding, continental climate

  24. val-24 · field trial

    Thermally Modified AshCentral Sweden, thermally modified hardwood cladding

    Mapped to Stockholm, Sweden (Dfb — humid continental) · north · sheltered · untreated

    inside P10–P90
    Observed
    30 yr
    source range 22–40 yr
    Modelled P50
    46.6 yr
    P10–P90 16.1–80 yr
    Blind (LOO)
    48.4 yr
    uncalibrated 68.5 yr · zone factor ×0.6906
    Residual
    +16.6 yr
    +55.3% of observed
    Observation ran
    14 yr
    source extrapolated beyond exposure

    Sheltered north exposure is the modification's best case; do not read it as a general figure.

    Source (peer reviewed): Nordic above-ground trials of thermally modified hardwoodScandinavian above-ground field trials of Thermowood class D hardwood cladding

Limits

What this benchmark cannot tell you

  • The sample is small and skewed to northern Europe. Aggregate metrics are indicative only.
  • Observations are digitised from published tables and figures; where a range was given, the midpoint is used.
  • Site climate is mapped to the nearest Köppen-equivalent reference climate, not the exact station. That mapping is part of the reported error.
  • Several sources extrapolate beyond their own exposure period. Those cases test the source's assumptions as much as the model's.
  • Failure criteria differ between sources — decay onset, serviceability, and replacement are not the same event.
  • The model is decay-led. In hot-arid zones the real failure mode is UV, checking and movement, which it under-weights.

The benchmark is versioned separately from the method so that accuracy can be tracked as both change. Corrections, additional field records and challenges to any case are welcome and will be credited in the next release.