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Life-Cycle Costing

Life-Cycle Costing is a procurement evaluation methodology that calculates the total cost of a product, service, or works contract across its full economic life, including acquisition, operation, maintenance, end-of-life disposal, and where methodologically established, external environmental costs such as greenhouse gas emissions.

Quick answer

Life-Cycle Costing is a procurement evaluation methodology that calculates the total cost of a product, service, or works contract across its full economic life, including acquisition, operation, maintenance, end-of-life disposal, and where methodologically established, external environmental costs such as greenhouse gas emissions.


Life-Cycle Costing (LCC) is a structured methodology for calculating the true economic cost of a procurement beyond the initial purchase price. It is particularly valuable for capital-intensive goods and infrastructure where operational and end-of-life costs can dwarf the acquisition cost over a multi-year contract horizon.

What is Life-Cycle Costing?

Articles 67 and 68 of Directive 2014/24/EU establish life-cycle costing as a legitimate basis for cost criterion evaluation in European public procurement. Article 68 specifies that life-cycle costs may include all or part of the following cost categories:

Costs borne by the contracting authority. These include costs relating to acquisition, use (such as energy consumption, maintenance, and end-of-life costs like collection, recycling, and disposal).

Environmental costs linked to the product or service. These cover the cost of greenhouse gas emissions and other pollutant emissions, and the cost of climate change mitigation. However, Article 68(2) requires that such environmental costs are expressed in monetary terms using a commonly accepted and verifiable methodology. The Commission has developed guidance on calculating carbon costs for road transport vehicles under the Clean Vehicles Directive (2009/33/EC, revised 2019/1161/EU), which provides a worked example of this approach.

The contracting authority must set out the full cost model in the procurement documents, specifying which cost elements are included, how they will be calculated, and what data bidders must supply. Fixed inputs (energy tariff, discount rate, utilisation assumptions) are typically authority-defined to ensure comparability. Variable inputs (projected maintenance costs, fuel or energy consumption per unit) are supplied by bidders based on their product specifications.

Life-cycle costing can be used in two ways. First, as the sole award criterion under the lowest cost criterion approach, where the compliant tender with the lowest LCC total wins. Second, as a component of a best price-quality ratio evaluation, where LCC forms the cost element and is weighted alongside quality criteria.

Why Life-Cycle Costing matters for bidders

LCC evaluation rewards suppliers whose products or services have superior operational efficiency. An energy-efficient vehicle fleet, low-maintenance infrastructure, or a software platform with minimal support overhead can produce a significantly lower life-cycle cost than a cheaper but less efficient alternative.

To compete effectively under LCC evaluation, bidders need accurate whole-life cost data for their products: energy consumption figures from certified testing, maintenance schedules and associated costs from service records, and disposal or decommissioning cost estimates. Bidders who can provide auditable, third-party-verified data for their cost inputs will be better positioned than those relying on unsubstantiated estimates.

Understanding the authority's cost model format is essential. An error in completing the cost template, or a figure that appears inconsistent with the specification, may trigger a non-compliant tender determination or an abnormally low tender query.

Example

A Danish regional authority procures 50 refuse collection vehicles. The procurement documents define a twelve-year LCC model covering purchase price, annual servicing costs per manufacturer specification, fuel or energy consumption per kilometre at a fixed tariff, tyre replacement intervals, and residual value at disposal. Bidders supplying electric vehicles with lower per-kilometre energy costs and lower servicing requirements produce a lower twelve-year total even at a higher purchase price than diesel alternatives.

Frequently Asked Questions

Is there a standard EU methodology for life-cycle costing?

Not a single universal standard, but several sector-specific methodologies exist. The Clean Vehicles Directive provides a prescribed LCC formula for road transport. The Commission's Green Public Procurement criteria include LCC guidance for specific product categories. ISO 15686 provides a general framework for buildings and infrastructure. Contracting authorities should specify which methodology they are using in the procurement documents.

Can bidders challenge the authority's cost model assumptions?

Bidders may raise questions during the clarification period before the tender deadline. They cannot unilaterally change authority-defined inputs, but if an assumption is demonstrably incorrect or discriminatory, a formal challenge to the procurement documentation may be possible. Once the tender period opens, the cost model is fixed.

Does LCC always benefit sustainable products?

Generally yes, where operational costs dominate the life-cycle. However, if the cost model does not capture the relevant efficiency parameters (for example, if energy costs are modelled at too low a tariff, or if the contract term is too short to amortise a higher purchase cost), a more efficient product may not produce a lower LCC score. Bidders should study the cost model carefully and, where appropriate, provide additional context in a cover letter or clarification response.

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