Michael Ashby's material-selection charts turned an abstract optimisation — choosing the best material for a function — into something an engineer could see: two properties on log–log axes, a guideline of the right slope, and the winning family lights up. This is Part 1 of a two-part note. It follows that idea through two more generations — a multi-objective value function for when one chart is not enough, and an eco-cost axis that turns the same method toward sustainability — and stops exactly where the two-dimensional chart itself starts to run out of room. Part 2, “Ashby's Maps, Renewed,” picks up from there with a generative, learned alternative.
Ashby developed a simple, powerful method for selecting materials in engineering design
Consider a panel of length
Everything in the first bracket is fixed by the design; only
That last sentence is worth deriving properly, because it is the whole reason the Ashby chart works at
all. Any index of the form
So on a chart of
| Loading case | Exponent | Index | Guideline slope |
|---|---|---|---|
| Tie, axial, stiffness-limited | 1 | 1 | |
| Beam or shaft, bending/torsion, stiffness-limited | 1/2 | 2 | |
| Panel, bending, stiffness-limited | 1/3 | 3 |
These are exactly the three guideline families printed on Ashby's own stiffness–density chart, and
the algebra generalises without change to any pair of properties: replace
But real components rarely answer to one objective. A tie that must also be cheap and light, a heat exchanger that must resist both thermal shock and corrosion — the moment a
second performance metric
With two performance metrics
Applied to a practical material selection problem — choosing a material that is both stiff
(
A trade-off surface narrows the field to good compromises but does not by itself choose one. Three strategies do: judgement (inspect and pick intuitively), constrain all-but-one objective and optimise the remaining one, or combine every objective into a single composite score — a value function.
1.3The coefficients
Exchange constants come from technical/economic modelling, historical price data etc.
Published values for weight-saving in transport span four orders of magnitude
Return to the panel and add cost as a second objective. From the mass performance equation, define
Since cost is one of the objectives,
| Material | ρ (Mg/m³) | E (GPa) | Cm (£/kg) | V, a1=0.5 | V, a1=500 |
|---|---|---|---|---|---|
| Cast iron, nodular | 7.30 | 175 | 0.25 | 0.98 | 652.9 |
| Low-alloy steel (4340) | 7.85 | 210 | 0.45 | 1.25 | 660.9 |
| Al 6061-T6 | 2.85 | 70 | 0.95 | 1.00 | 346.4 |
| Al-6061-20%SiC, PM | 2.77 | 102 | 25.0 | 15.12 | 311.2 |
| Ti-6-4, B265 grade 5 | 4.43 | 115 | 20.0 | 18.68 | 473.7 |
| Beryllium, SR-200 | 1.84 | 305 | 250.0 | 68.47 | 205.0 |
At low
Beyond two objectives the graphical tangent-line construction stops being practical; the paper's own
answer is to rank candidates directly by
An eco-cost is the amount of money that would have to be spent today, with best
available technology, to prevent an environmental burden from exceeding what the Earth can carry in the
long run
The same logic applies to every impact category — acidification, eutrophication, toxicity,
resource depletion, land use — each with its own prevention cost, summed into a single monetary
eco-cost per kilogram. Expressing environmental impact this way, rather than in physical units or
dimensionless “points”, buys comparability across categories, plain communication to
engineers who already think in cost, and transparency: every number traces back to an explicit,
auditable prevention technology, unlike the less transparent weighting schemes used in classical Life
Cycle Assessment
A lower EVR means the same customer value at a smaller environmental burden. The eco-costs framework
extends the Ashby method by replacing (or complementing) the price axis with the
eco-cost per unit volume,
A lower index means a more eco-efficient choice for that structural function: the same mechanical performance for a smaller environmental prevention cost.
| Material | ρ (kg/m³) | E (GPa) | σy (MPa) | eco-cost (€/kg) | IE | Iσ,bend |
|---|---|---|---|---|---|---|
| Structural wood | 500 | 10.0 | 40 | 0.05 | 7.9 | 2.1 |
| Concrete | 2400 | 30.0 | 30 | 0.02 | 8.8 | 5.0 |
| Mild steel | 7850 | 210.0 | 250 | 0.40 | 216.7 | 79.1 |
| Aluminium alloy | 2700 | 70.0 | 100 | 1.00 | 322.7 | 125.3 |
| PET plastic | 1350 | 2.8 | 55 | 0.60 | 484.1 | 56.0 |
| GFRP composite | 1800 | 20.0 | 200 | 1.50 | 603.7 | 78.9 |
Two things stand out, typical of real eco-Ashby analyses: low-tech, low-processing materials such as wood and concrete carry very low eco-costs per kilogram, often outweighing their modest mechanical properties; metals and engineered composites, although mechanically excellent, carry a much higher environmental prevention cost per unit of stiffness or strength delivered.
This is the added value of eco-Ashby charts: they let a designer ask not just “which material is technically best?” but “which material achieves this technical performance at the lowest environmental prevention cost?” — using the same intuitive, visual method engineers already trust.
2Three generations of the same idea sit side by side in this note. The chart compresses a mechanics derivation into a slope on two log axes — unbeatable for one index, incapable of more than two properties at a time. The value function removes this limitations by aggregating any number of objectives into one weighted sum, at the cost of losing visual representation: beyond two dimensions, Ashby's own method falls back to a table and a ranking, as §1.4 showed directly. The eco-Ashby chart does not change the mathematics at all — it changes what one of the axes is allowed to mean, substituting a rigorously defined environmental prevention cost for price, and in doing so turns “which material is best?” into “best for whom, and at what true cost?” without asking the designer to learn a new method.
What all three share is a hard limit: every one of them still needs a human to pick the axes, and the moment a design question genuinely depends on three, four, or six properties at once — a spring that must be light and strong and cheap, a heat exchanger balancing thermal shock against corrosion — the chart runs out of dimensions and the value function runs out of picture. That is precisely where this note stops being about charts and starts being about search.
Part 2, “Ashby's Maps, Renewed,” takes the same 22-material database this article has used throughout and trains a variational autoencoder on it — a continuous, differentiable stand-in for the discrete chart, searched by gradient ascent rather than read by eye. The two baseline cases worked by hand in §1.1 above, the stiffness-limited bar and the deflection-limited beam, are the first thing Part 2 checks the learned model against.
Joseph Morlier (ISAE-SUPAERO) posed the extension and supplied the source notebooks and LaTeX notes underlying this article. The interactive chart widget and the eco-costs/eco-Ashby derivations were drafted with Claude.
Figures are reproduced from eco_costs_and_ashby_charts.ipynb and
ashby_method_step_by_step.ipynb. Material-property and eco-cost figures used in this
article's worked examples are illustrative, order-of-magnitude values for teaching, not authoritative
Idemat/CES data.
This is Part 1 of a two-part note. Part 2, “Ashby's Maps, Renewed,” extends the same material database and the same case studies to a generative, VAE-based latent space, searched by gradient ascent instead of read off a log–log chart.