Handbook on environmental assessment of products

2. Describe the product life-cycle

2.1 Define your task
2.1.1 Where in the life-cycle are the significant environmental impacts found?
2.1.2 Use a chart for your planning
2.1.3 Information about disposal and transport
2.1.4 What should be included?
2.2 Collect data for the product life-cycle
2.2.1 Would a flow diagram of the product  life-cycle be more suitable?
2.2.2 Compensation

Once you know exactly what the product delivers to users and what its secondary services are, you need to find out what the environmental impacts of the produc are. The first step in this regard is to form an overview of the product life-cycle.

2.1 Define your task

A product life-cycle has five main phases: the raw materials phase, the production phase, the use phase, the disposal phase, and the transport phase. Transport can either be dealt with separately or be distributed among the other phases.

2.1.1 Where in the life-cycle are the significant environmental impacts found?

Begin by noting down the product life-cycle on a piece of paper. Try to form an impression of the significant and insignificant issues associated with the product life-cycle. Assess the total weight of the product and the types of raw materials used. Consider whether production of the product might entail particularly problematic processes or chemicals. Examples would be use of varnishes that emit solvents or particularly energy-intensive processes such as enamelling.

Look at the product lifespan: for most products, the use phase is much longer than the other phases. Thanks to modern technology, the total working time spent on making a coffee maker is less than an hour, while its expected lifespan is five years, perhaps even more. Try to apply proportions to the use phase. Consider the most likely route of disposal of the product: which materials will be recycled? Which

2.1.2 Use a chart for your planning

Think about how you can get the data you need, and how you will go about collecting data. You can use a chart such as the one for the coffee maker shown in table 2.1 as the basis for your deliberations and planning.

Table 2.1
Initial overview of the lifecycle of a coffee maker

Phase

Description

Where can data be found?

Raw materials phase

Total product weight: a couple of kg.

Material contents: plastic, glass, steel, aluminium, copper (in wires), materials for the heating element (?)

Packaging: cardboard (probably recycled).

Production department, raw materials and process lists.

Production phase

Most significant production processes: shaping the raw materials, e.g. aluminium moulding. Surface treatment of steel parts.

Special processes/chemicals: heavy metals for surface treatment. Possibly other processes as well – check.

Production department, raw materials and process lists. Data on chemicals can also be found with the environmental department// occupational health service.

Use phase

Life span: estimated at five years on average.

Sales by markets/countries (>80%): Denmark, Sweden, Norway, and Germany.

Operation

Operation data: a total of 2 x 7 x 52 x 5 = 3,640 litres of coffee made. Total time per litre: approximately 12 minutes. The coffee is kept hot (80ºC) for approximately 30 minutes on average.

Energy consumption: 3,640 litres of coffee is heated from approximately 10ºC to boiling point. Heating losses from 1 litre of very hot water for a total of 1,820 hours.

Raw materials consumption: 3,640 coffee filters and a quantity of coffee.

Consumption of ancillary materials: no.

Maintenance

Energy consumption: decalcification involves heating of 2 litres of water to boiling point once a month (?)

Cleaning of pot and machine with warm water – how often?

Raw materials consumption: no.

Consumption of ancillary materials: vinegar (for decalcification), soap/washing-up liquid (for cleaning).

Sales and marketing department

Dealers

Product-development department.

Disposal phase

Ways of disposal, estimated average (%)

Disposal takes place through recycling stations or via household garbage bins.

Landfills: estimated at 0%

Incineration: estimated at 100% of all machines and 50% of all pots. Their energy content is utilised.

Shredding: estimated at 0%

Separation: estimated at 0%

Recycling: 50% of all glass pots are estimated to be recycled

Other: estimated at 0%

Possibly the sales and marketing department and the product-development department.

Possibly with the local authorities, e.g. recycling depots.

Possibly with knowledge institutes.

Transport phase

The coffee is transported 10,000 km.

The raw materials for the coffee maker are transported 2,000 km to the manufacturer.

The finished coffee maker is transported 100 km to the consumer. When the consumer eventually throws it out, it will be transported 5 km for disposal.

Possibly with the sales and marketing department.


Example B2.1: Sportswear

A company which manufactures sportswear switched to a type of fibre which reduced energy consumption by half in the manufacturing process. This was regarded as a considerable environmental improvement of the product. However, the company was subsequently asked how many times the garments were washed and tumble dried throughout their lifespan and about the differences between the old and new fibre types in terms of their ability to retain water, hence their impact on the energy needed to tumble dry them. It turned out that no account had been taken of this.


Some products are "active" during the use phase, e.g. energyconsuming products such as vacuum cleaners, computers, television sets, or pumps. For other products, the use phase involves very frequent maintenance, e.g. textile products or tableware. For such products, the use phase is almost always dominant. Other products are more "passive", which is to say that they do not have the same degree of impact on the environment during the use phase, e.g. furniture, newspapers, packaging, or paper cups. Even passive products may, however, involve some environmental impact during the use phase: furniture and other objects may need cleaning, maintenance, cooling, heating, drying or similar, and they may exercise an indirect impact on the environment because they form part of other systems. This is why you need to take a very careful look at the entire product life-cycle, trying to imagine all the processes the product goes through and the impacts it causes.

2.1.3 Information about disposal and transport

It can be difficult to obtain specific figures for disposal and transport. Waste from private households is disposed of through standard household waste or via a recycling depot. You can safely assume that all waste which is being disposed of as part of the standard household waste will be incinerated 100%. For waste delivered to recycling depots, you can use the values given in table 2.2. These values are approximate and should only be used if you do not have more detailed information to hand from other sources. Actual disposal will depend on factors such as:
Opportunities for separation
Collection systems
Economically feasible reprocessing techniques

Table 2.2
Rules of thumb for disposal routes for raw materials disposed of via recycling depots

 

Incineration

Reuse

Landfilling

Paper/cardboard (packaging)

25

75

0

Plastic

85

15

0

Metal

0

100

0

Glass

0

100

0

Non-flammable waste

0

0

100


2.1.4 What should be included?

You will often have to decide whether you should include minor parts of the product in your considerations, e.g. screws, oil, and similar. In the example of the coffee maker, you may also want to include coffee filters and the coffee itself. If you are not sure what to include, assume that anything which is influenced by the company's or the user's choices must be included.

There are no fixed criteria to decide on what should be included. What you need to do is to cover a significant part of the life-cycle. One possibility is to look at the product weight. For example, you may decide that at least 95% of the product weight must be covered by the environmental assessment. However, even small parts can contribute significantly to energy consumption and/or environmental loads, so just looking at the weight is not enough.


So we cannot say, for example, that screws should never be considered. If your environmental assessment concerns a screw, it is obviously significant. If, however, you have a product which contains 100 kg steel and has a chromium-plated surface, 20 grams of steel screws do not make much difference. Omitting them from your assessment does not matter, because steel does not contain scarce resources or hazardous/harmful substances.

2.2 Collect data for the product life-cycle

You now need to obtain data about the entire product life-cycle. For example, you may want to collect data in tables to make them easily accessible to others. This will also make it easier to show what you have included in your environmental assessment. Information on raw materials and production will often be available from the company production department. Many companies have a so-called raw materials and process list which includes all the data you need. Information on where the product is sold is often available from the sales and marketing department, while data on the actual use can be collected from the sales staff and product-development staff alike. It will often be necessary to obtain information on disposal of the product from other sources, e.g. from the local recycling depots, from dealers (who sometimes receive returns of old product when selling new ones), or from knowledge institutes.

Example B.2.2: The coffee maker

The use phase: You might be able to get data on the use process from the marketing department, but it will often be necessary to carry out calculations on the basis of specifications and rating plates. The heating coil of the coffee maker has an effect of 600 W, and it takes approximately 12 minutes to make 1 litre of coffee. This means that the energy consumed to make coffee is 0.660 kW times 0.2 hours times 3,640 litres, corresponding to around 440 kWh to make 3,640 litres of coffee throughout the product lifetime. The effect of the hot plate is 55 W. Each pot of coffee is kept warm for 30 minutes (on average), corresponding to 0.5 hours times 0.055 kW times 3,640 = 100 kWh. This equals an energy consumption of 100 + 440 = 540 kWh. You should also remember that the coffee and coffee filters are part of the use phase. You may well ask yourself if you really need to include these things when you are supposedly looking at the coffee maker and the coffee maker is the only thing manufactured by your company. However, as the choice of concept and construction of the coffee maker can affect the use of filters and coffee, they do need to be included in the assessment so that we can see the environmental consequences of any changes.

The disposal phase: Disposal can be presented as shown in table 2.5. In this example, the entire product is sent for incineration via the standard household waste, except the glass pots; we assume that 50% of all glass pots are recycled. We will compensate for the recycled materials in our calculations of the total impact assessment. The steel parts are assumed to be sent for incineration, but at the same time half of this steel is assumed to be separated out on a sorting conveyor belt by means of magnets. It will then be sent for recycling. The table includes the concept "compensation" – this will be explained later.


Table 2.3
Composition of the coffee maker and the manufacturing processes associated with it

Components

Number

Raw materials

Weight

Manufacturing processes

Ancillary materials

Cabinet

1

Plastic, impactresistant polystyrene

1.1

Die casting
Pressure-die

Release agent

 

1

Aluminium

0.1

Casting

Lubrication?

 

1

Steel

0.3

Sheet-metal stamping
Punching

?

Wire

1

Copper

0.02

Wire drawing

 

 

1

Plasticized PVC

0.02

Coating

 

Glass pot

1

Glass

0.34

Glass moulding

 

Handle

1

Plastic, impactresistant polystyrene

0.02

Die casting

Release agent

Clamp

1

Aluminium

0.01

Rolling

?

Packaging

1

Cardboard

0.39

-

?


Table 2.4
Use of the coffee maker

Material/ component

Process

   

Ancillary materials

Name

Unit

Quantity

Name

Entire product

Coffee-making

Electricity consumption

Coffee filters

Coffee

Water

   

-

kWh

540

-

kg

7.3

Bleach

kg

290

Pesticides/fertilizer

kg

3,640

-

Cleaning (machine and pot)

kg

50

Water (hot/warm)

ml

25

Washing-up liquid

Decalcification

kg

15

Acetic acid

Compensation for heating

kWh

-360

-


Table 2.5
Disposal of the coffee maker

Component

Process

Ancillary material

Share

Name

Unit

Quantity

Name

Aluminium

1

Waste incineration, aluminium

kg

0.1

?

Polystyrene

1

Waste incineration, polystyrene

kg

1.1

?

 

1

Compensation for heat generated by waste incineration

kg

-1.1

?

Glass

0.5

Waste incineration, glass

kg

0.17

?

 

0.5

Melting, glass

kg

0.17

?

 

0.5

Compensation for glass

kg

-0.17

?

Steel

1

Waste incineration, steel

kg

0.3

?

 

0.5

Melting, steel

kg

0.15

?

 

0.5

Compensation for steel

kg

-0.15

?

Copper

1

Waste incineration, copper

kg

0.02

?

Coffee filters

1

Waste incineration, coffee filters

kg

7.3

?

 

1

Compensation for heat generated by waste incineration

kg

-7.3

?

Coffee grinds

1

Waste incineration, organic materials

kg

290

?

 

1

Compensation for heat generated by waste incineration

kg

-290

?

Packaging

1

Waste incineration, cardboard

kg

0.39

?

 

1

Compensation for heat generated by waste incineration

kg

-0,39

?


Include a conservative calculation of the significance of the total transport to get an initial impression of whether transport is important to the overall situation. In most cases, transport is not very important, and optimisation within this area can often be left to the logistics department. Transport for the coffee maker is illustrated in table 2.6.

Table 2.6
Transport, coffee maker

Mode of transport

Distance, km

Quantity, kg

Transport of coffee, ship

10,000

90,0

Transport of raw materials for coffee maker, car

2,000

2.3

Transport of coffee maker to user, car

100

2.3

Transport of coffee maker for disposal, car

5

2.3


Tables 2.3-2.6, illustrated here by our example of the coffee maker, form the basis for your environmental assessment. They specify all the information you need about the product and its life-cycle. You will often need various data, particularly in connection with processes and ancillary materials – this is also illustrated in the example of the coffee maker. You will have to leave these matters aside for the present, but they should still be included in your basis for future work, as they will be addressed at a later stage.

It is important that you indicate very clearly what you have included in your environmental assessment. Place checkmarks in your tables or make a list of your omissions and assumptions.


2.2.1 Would a flow diagram of the product life-cycle be more suitable?

Would a flow diagram of the product life-cycle be more suitable? The raw materials and process list model can be useful for establishing an overview of the product life-cycle if the product in question comprises many separate components and/or raw materials. For simpler and more homogenous products, you can also choose to use a flow diagram. In some cases, such a diagram provides a better overview. You are free to choose whatever you feel is best in each case.

Figure 2.1
Overview of the coffee maker's life-cycle. Transport not included.

2.2.2 Compensation

In the previous section, we mentioned that the unintentional secondary services seen in connection with most products often have considerable impact on the environment. This kind of service appears where the system that you are looking (the product life-cycle and the processes it includes) affects or is connected to other systems. Secondary services reduce or eliminate the need for alternative ways of receiving the service in question. In order to take this into account, we need to compensate for such services. If, for example, metals are being recycled, you need to deduct production of a corresponding amount of metal from the overall result. This means that for the purpose of calculations, you will experience negative raw materials consumption during the disposal phase.

Compensation occurs most frequently within the following areas:
Excess heat from electrical appliances and devices
Electricity and heating generated by means of waste incineration
Recycling

Excess heat is typically encountered during the use phase and constitutes a negative contribution. It is important to address excess heat separately, as this is one of the areas where your work can make a difference. For coffee makers and water heaters, excess heat represents the greatest scope for improvements.

In Denmark, the heat generated by incineration plants is utilised. The heat which can be utilised corresponds to the calorific value of the materials. Plastic and papier are high-grade fuels, while metals usually have no calorific value. The values can be found in Appendix B, table 2.1.

When materials are recycled, this is indicated by placing a – in front of the recycled materials during the disposal phase. Remember to include energy consumption for the recycling process in your calculations (e.g. melting). It is not enough to simply hand over the materials; they also need to be processed.

Remember that compensation can only be carried out in situations where, for example, materials are in fact recycled or are very likely to be recycled. It is not enough that they can be recycled.

Table 2.7
A product contains 10 kg plastic, of which 5 kg are recycled

Example B2.3: Compensation
A product contains 10 kg plastic, of which 5 kg are recycled.

 

The raw materials phase

The disposal phase

Raw materials

10 kg plastic (resources)

5 kg plastic (resources)

Energy

10 kg plastic (energy)

Energy for reprocessing of 5 kg plastic