PRIMES [6] Life Cycle Costs (LCC) in GPP Presented by
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Overview
LCC - the real price of products
How to use LCC in public procurement
When to use LCC in public procurement
LCC methodology/tools
Good practice examples
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Overview How much does a product cost?
Disposal
Use
Cost
Use
Disposal
Price
Standard product
Price
Green product
Changing mindset
Cheapest price
Economically most advantageous offer
Life Cycle Costing (LCC) Covers the entire lifecycle of a product or provision of a service, from raw material to disposal/recycling
Before use – Development, production and procurement
During use – operation with operating costs, service and usage of resources
After use – recovery with disposal, recycling or sales revenue Source: Baltic GPP Green Public Procurement PPT– www.balticgpp.eu
Life Cycle Costing (LCC)
Source: SMART SPP project – www.smart-spp.eu
Use of LCC in public procurement BENEFITS
Greater awareness of total costs
Greater transparency of future costs
Better prediction and planning
Helps on evaluation of bids in a more sustainable manner
More efficient use of public resources
Greater awareness and communication of savings
Source: © SMART SPP Project - www.smart-spp.eu
LCC, LCA and TCO Terminology
Life Cycle Costing (LCC): technique considering costs and benefits taking place during a specific phase of the lifecycle of a product
Life Cycle Assessment (LCA): considers the environmental impact of a product from cradle to grave.
Total Cost of Ownership (TCO): includes only direct costs for the owner of the product (purchasing price + cost of use + disposal)
The real costs Internal & External costs External costs Social costs: environmental damage, climate change, biodiversity loss, health issues
Advanced LCC
Internal costs TCO (price, usage, maintenance, disposal)
Conventional LCC
External LCC costs
= LCC which monetises environmental externalities [Whole-life costing” (WLC)]
= costs for society of specific environmental impacts, such as climate change or acidification.
Use of LCC in top ten EU MS
Source: 2012, CEPS, The uptake of green public procurement in the EU 27
Overview
LCC - the real price of products
How to use LCC in public procurement
When to use LCC in public procurement
LCC methodology/tools
Good practice examples
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
EU Procurement Directive Requirements (Directive 2004/24, art. 68) I
Costs related to environmental externalities can only be taken into account if their monetary value can be determined and verified.
In order to ensure that LCC is transparent and embodies equal treatment, the methodology (LCC tool used) must be indicated in advance in the tender
documents and accessible to all interested parties.
EU Procurement Directive Requirements (Directive 2004/24, art. 68) II
The methodology must be based on objectively verifiable and non-discriminatory criteria and the data required can be provided with reasonable effort by 'normally diligent' operators, including those from outside of the EU.
Whenever a common method for the calculation of life- cycle costs has been made mandatory by a legislative act of the Union, that common method shall be applied for the assessment of life-cycle costs (e.g. Clean Vehicles Directive).
The Clean Vehicle Directive External LCC costs
Contracting authorities must take energy and environmental
impacts into account when purchasing road transport vehicles (either in specifications or award criteria)
Provides methodology for the monetisation of these impacts
Model allocates a monetary value to several types of emission – carbon dioxide (CO2), nitrous oxide (NOx), non-methane hydrocarbons (NMHC) and particulate matter
Cost of lifetime emissions of each vehicle tendered to be added to other direct costs such as purchase price, fuel costs and maintenance.
LCC considerations (I) Savings on use of energy and water
Need of energy and water => strong impact on LCC costs
Need of energy and water => strong environmental impact
Greek city saves on lighting costs The City of Amaroussion in Greece examined the potential savings from replacement of its street lighting equipment before going to tender. It found that replacement of its old high-pressure mercury lamps with metal halide lamps would lead to savings of approximately 40% per annum in terms of electricity consumption.
Source: Buying Green! A handbook on green public procurement 2nd edition, European Commission 2011
LCC considerations(II) Savings on maintenance and replacement
maximise the period until replacement
minimise the amount of maintenance work which needs to be done.
Innovative example! The use of ground granulated blast furnace slag in concrete may increase the lifespan of buildings, and at the same time reduce the amount of efflorescence (saltpetering) requiring maintenance. This could reduce the total life-cycle cost when compared with other types of concrete. consumption.
Source: Buying Green! A handbook on green public procurement 2nd edition, European Commission 2011
LCC considerations(III) Savings on disposal costs
Often underestimated!
Can turn a bargain into an expensive purchase.
Range from cost of physical removal to paying for secure disposal.
Intelligent planning in building sector In your call for tenders you could ask builders how much hazardous waste they expect to produce during demolition and the cost of removing it. In some cases, e.g. road building, it should also be possible to calculate the profits to be made from using recycled waste materials, such as used asphalt or demolished building materials.
Source: Buying Green! A handbook on green public procurement 2nd edition, European Commission 2011
LCC considerations(IV) Discount rate and data availability Discount rate
Costs in the future are not worth as much as those incurred today
Net present value: e.g. 1000€ invested today at 3% interest would be worth 1030€ in 1 years‘s time. Therefore, 1030€ spent in 1 year‘s time is only worth 1000€ at present time.
Data availability and reliability
Unpredictability of costs to be incurred in the future needs independent, reliable cost estimates (e.g. future trend of fuel prices)
LCC considerations(V) Data needed for calculations
A breakdown of the various costs of the product or service
An estimate of all costs
The discount rate and the inflation rate for the different cost
elements
The time frame in order to calculate the present net value of the the product or service
Overview
LCC - the real price of products
How to use LCC in public procurement
When to use LCC in public procurement
LCC methodology/tools
Good practice examples
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Use of LCC in public procurement EX ANTE (pre-tendering phase) Before the tendering procedure to:
help defining needs
decide on the best available environmental and economic option to tender (planning)
Example:
Provide public transport tickets for administration instead of purchasing new cars
Use of LCC in public procurement DURING the tendering procedure During the tendering procedure to:
compare the economic offers of products and services
Example: Assign a higher amount of awarding points to offers/bids with lower LCC
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Use of LCC in public procurement EX POST After the tendering procedure to:
assess choice green vs. standard product
inform on the benefits obtained
gather information and enable better future planning
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Overview
LCC - the real price of products
How to use LCC in public procurement
When to use LCC in public procurement
LCC methodology/tools
Good practice examples
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
The Smart SPP LCC/CO2tool
Microsoft Excel® Tool (html-version: www.lcc-tool.eu)
Supports procurers in calculating life-cycle costs and CO2 emissions of innovative products and services
Graphical display of results and tender evaluation (up to 15 offers)
Source: © SMART SPP Project - www.smart-spp.eu
The BUY SMART+ tool
Tool produced within EU-Project „Buy Smart+ Green Procurement in Europe“ (IEE EC Funding programme)
General calculation tool to be used for electricity using products
Website: http://www.buy-smart.info/downloads2/downloads3
Source: Buy Smart+ at www.buy-smart.info
The Swedish Environmental Management Council (SEMCO)
SEMCO has developed several excel tools for calculating LCC in public procurement.
In addition to a general tool, specialised ones are available for professional kitchens (fridges and freezers), indoor and outdoor lighting and vending and coffee machines, light vehicles
Website: http://www.msr.se/en
The ENERGY STAR ® tool
Energy Calculator for PC Equipment
Website: http://www.eu-energystar.org/en/en_008.shtml
Overview
LCC - the real price of products
How to use LCC in public procurement
When to use LCC in public procurement
LCC methodology/tools
Good practice examples
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Kolding, Denmark Interior and external lighting
Founding member of :
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Kolding, Denmark Good practice example Introduction:
Procurement of innovative, energy efficient LED replacement light bulbs, for indoor and outdoor use
aims to encourage sustainable product innovation for energy efficient lighting technologies
Tender was devided in three sub-groups: low voltage lights bulb, 230 volt halogen light bulbs and pins, 230 volt light bulbs
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Kolding, Denmark Technical specifications: Indoor lighting CRI (Colour Rendering Index)>80 Colour temperature (Kelvin) 2700-3000 General lighting-efficiency (lumen/watt)> 50 Effect lighting -efficiency (lumen/watt)> 40 Life-span (hours at L70)> 20000
Outdoor lighting CRI (Colour Rendering Index)>75 Colour temperature (Kelvin) 3000-4000 General lighting-efficiency (lumen/watt)> 50 Life-span (hours at L70)> 20000 Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Kolding, Denmark Award criteria:
Life-cycle costs have been given a weighting of 55%. These are broken down by: purchase price (35%), lifetime (35%) and operating costs (30%)
Energy-efficiency (lumen/watt) (25%)
Light quality (CRI) (20%)
Results:
The deadline for responding to the call for tender is set for the end of February. The results of the tender will be available on
the SMART SPP website when the process is completed. Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net
Berlin, Germany Vehicles
© http://it.gdefon.com/download/vista_Strada_viale_Berlino_parco/411414/3000x1988
Berlin, Germany Good practice example Introduction:
procures a variety of vehicles every year (approximately 200)
considering life cycle costs in the procurement process of vehicles to include energy and environmental costs.
sustainability criteria included based on those required by the Clean Vehicles Directive and were developed in further detail to
meet the needs of the police force and adjusted to the current status quo of vehicle technology
Berlin, Germany Technical specifications:
Meeting German 4 standard for particle emissions – this allows the vehicle to be driven in German inner-city environmental zones (‘Umweltzone’)
Carbon particulate filter (for diesel engines)
Meeting the Euro 5 European Emission Standard (the most
demanding standard at the time of tendering)
Berlin, Germany Award criteria I: The tender was awarded using a two-step process: 1) Assessment of technical aspects (40% of total points) and LCC (60% of total points), which includes financial and environmental costs. A maximum of 40,000 points could be awarded. 2) The highest scoring bid from step 1, along with the bids which scored up to 10% less points, were then compared purely on the basis of their purchase price, awarding the tender then to the lowest bid.
Berlin, Germany Award criteria II: LCC including environmental costs: Maintenance costs were calculated based on calculations made using co-efficients for future specific maintenance and repair work of the vehicles (e.g. tyres, window replacement). The environmental costs were calculated based on a) fuel consumption, b) energy consumption, c) CO2 emissions, d) NOx, e) non-methane hydrocarbons and f) particulate matter. The lifetime cost calculation from the Clean Vehicles Directive was largely used as a basis for calculating the environmental costs.
Berlin, Germany Results: There were no problems encountered with bidders being unable to conform or meet the tender requirements. Also, the total number of bids received did not differ to the number received from previous tenders. Due to the strict focus and the consideration of the various costs during the products lifetime, the tender was awarded to the bidder who successfully complied with the predetermined environmental criteria and also satisfied the financial requirements imposed, thus also obtaining a positive economic result for the tendering authority.
Source: © Image courtesy of Stuart Miles at FreeDigitalPhotos.net