One of the main sinks of energy in the “developed” world is the creation of stuff. In its natural life cycle, stuff passes through three stages. First, a new-born stuff is displayed in shiny packaging on a shelf in a shop. At this stage, stuff is called “goods.” As soon as the stuff is taken home and sheds its packaging, it undergoes a transformation from “goods” to its second form, “clutter.” The clutter lives with its owner for a period of months or years. During this period, the clutter is largely ignored by its owner, who is off at the shops buying more goods. Eventually, by a miracle of modern alchemy, the clutter is transformed into its final form, rubbish. To the untrained eye, it can be difficult to distinguish this “rubbish” from the highly desirable “good” that it used to be. Nonetheless, at this stage the discerning owner pays the dustman to transport the stuff away.
Figure 15.1: Selfridges’ rubbish advertisement.
Let’s say we want to understand the full energy-cost of a stuff, perhaps with a view to designing better stuff. This is called life-cycle analysis. It’s conventional to chop the energy-cost of anything from a hair-dryer to a cruise-ship into four chunks:
Phase R: Making raw materials. This phase involves digging minerals out of the ground, melting them, purifying them, and modifying them into manufacturers’ lego: plastics, glasses, metals, and ceramics, for example. The energy costs of this phase include the transportation costs of trundling the raw materials to their next destination.
embodied energy (kWh per kg)
Embodied energy of materials.
Phase P: Production. In this phase, the raw materials are processed into a manufactured product. The factory where the hair-dryer’s coils are wound, its graceful lines moulded, and its components carefully snapped together, uses heat and light. The energy costs of this phase include packaging and more transportation.
Phase U: Use. Hair-dryers and cruise-ships both guzzle energy when they’re used as intended.
Phase D: Disposal. This phase includes the energy cost of putting the stuff back in a hole in the ground (landfill), or of turning the stuff back into raw materials (recycling); and of cleaning up all the pollution associated with the stuff.
To understand how much energy a stuff’s life requires, we should estimate the energy costs of all four phases and add them up. Usually one of these four phases dominates the total energy cost, so to get a reasonable estimate of the total energy cost we need accurate estimates only of the cost of that dominant phase. If we wish to redesign a stuff so as to reduce its total energy cost, we should usually focus on reducing the cost of the dominant phase, while making sure that energy-savings in that phase aren’t being undone by accompanying increases in the energy costs of the other three phases.
Rather than estimating in detail how much power the perpetual production and transport of all stuff requires, let’s first cover just a few common examples: drink containers, computers, batteries, junk mail, cars, and houses. This chapter focuses on the energy costs of phases R and P. These energy costs are sometimes called the “embodied” or “embedded” energy of the stuff – slightly confusing names, since usually that energy is neither literally embodied nor embedded in the stuff.
Let’s assume you have a coke habit: you drink five cans of multinational chemicals per day, and throw the aluminium cans away. For this stuff, it’s the raw material phase that dominates. The production of metals is energy intensive, especially for aluminium. Making one aluminium drinks-can needs 0.6 kWh. So a five-a-day habit wastes energy at a rate of 3 kWh/d.
As for a 500 ml water bottle made of PET (which weighs 25 g), the embodied energy is 0.7 kWh – just as bad as an aluminium can!
Figure 15.3: Five aluminium cans per day is 3 kWh/d. The embodied energy in other packaging chucked away by the average Brit is 4 kWh/d.
The average Brit throws away 400 g of packaging per day – mainly food packaging. The embodied energy content of packaging ranges from 7 to 20 kWh per kg as we run through the spectrum from glass and paper to plastics and steel cans. Taking the typical embodied energy content to be 10 kWh/kg, we deduce that the energy footprint of packaging is 4 kWh/d. A little of this embodied energy is recoverable by waste incineration, as we’ll discuss in Chapter Five energy plans for Britain.
Making a personal computer costs 1800 kWh of energy. So if you buy a new computer every two years, that corresponds to a power consumption of 2.5 kWh per day.
Figure 15.4: She’s making chips. Photo: ABB. Making one personal computer every two years costs 2.5 kWh per day.
The energy cost of making a rechargeable nickel-cadmium AA battery, storing 0.001 kWh of electrical energy and having a mass of 25 g, is 1.4 kWh (phases R and P). If the energy cost of disposable batteries is similar, throwing away two AA batteries per month uses about 0.1 kWh/d. The energy cost of batteries is thus likely to be a minor item in your stack of energy consumption.
Newspapers, magazines, and junk mail
A newspaper, distributed for free at railway stations, weighs 90 g. The Cambridge Weekly News (56 pages) weighs 150 g. The Independent (56 pages) weighs 200 g. A property-advertising glossy magazine and Cambridgeshire Pride Magazine (32 pages), both delivered free at home, weigh 100 g and 125 g respectively.
This river of reading material and advertising junk pouring through our letterboxes contains energy. It also costs energy to make and deliver. Paper has an embodied energy of 10 kWh per kg. So the energy embodied in a typical personal flow of junk mail, magazines, and newspapers, amounting to 200 g of paper per day (that’s equivalent to one Independent per day for example) is about 2 kWh per day.
Paper recycling would save about half of the energy of manufacture; waste incineration or burning the paper in a home fire may make use of some of the contained energy.
The largest stuff most people buy is a house.
In Chapter Stuff II, I estimate the energy cost of making a new house. Assuming we replace each house every 100 years, the estimated energy cost is 2.3 kWh/d. This is the energy cost of creating the shell of the house only – the foundation, bricks, tiles, and roof beams. If the average house occupancy is 2.3, the average energy expenditure on house building is thus estimated to be 1 kWh per day per person.
What about a car, and a road? Some of us own the former, but we usually share the latter. A new car’s embodied energy is 76000 kWh – so if you get one every 15 years, that’s an average energy cost of 14 kWh per day.
A life-cycle analysis by Treloar, Love, and Crawford estimates that building an Australian road costs 7600 kWh per metre (a continuously reinforced concrete road), and that, including maintenance costs, the total cost over 40 years was 35000 kWh per metre. Let’s turn this into a ballpark figure for the energy cost of British roads. There are 28000 miles of trunk roads and class-1 roads in Britain (excluding motorways). Assuming 35000 kWh per metre per 40 years, those roads cost us 2 kWh/d per person.
Transporting the stuff
Up till now I’ve tried to make estimates of personal consumption. “If you chuck away five coke-cans, that’s 3 kWh; if you buy The Independent, that’s 2 kWh.” From here on, however, things are going to get a bit less personal. As we estimate the energy required to transport stuff around the country and around the planet, I’m going to look at national totals and divide them by the population.
Figure 15.5: Food-miles – Pasties, hand-made in Helston, Cornwall, shipped 580 km for consumption in Cambridge.
Freight transport is measured in ton-kilometres (t-km). If one ton of Cornish pasties are transported 580 km (figure 15.5) then we say 580 t-km of freight transport have been achieved. The energy intensity of road transport in the UK is about 1 kWh per t-km.
Figure 15.6: The container ship Ever Uberty at Thamesport Container Terminal. Photo by Ian Boyle www.simplonpc.co.uk.
When the container ship in figure 15.6 transports 50000 tons of cargo a distance of 10000 km, it achieves 500 million t-km of freight transport. The energy intensity of freight transport by this container ship is 0.015 kWh per t-km. Notice how much more efficient transport by container-ship is than transport by road. These energy intensities are displayed in figure 15.8.
Transport of stuff by road
In 2006, the total amount of road transport in Britain by heavy goods vehicles was 156 billion t-km. Shared between 60 million, that comes to 7 t-km per day per person, which costs 7 kWh per day per person (assuming an energy intensity of 1 kWh per ton-km). One quarter of this transport, by the way, was of food, drink, and tobacco.
Figure 15.7: The lorry delivereth and the lorry taketh away. Energy cost of UK road freight: 7 kWh/d per person.
Transport by water
In 2002, 560 million tons of freight passed through British ports. The Tyndall Centre calculated that Britain’s share of the energy cost of international shipping is 4 kWh/d per person.
Transport of water; taking the pee
Water’s not a very glamorous stuff, but we use a lot of it – about 160 litres per day per person. In turn, we provide about 160 litres per day per person of sewage to the water companies. The cost of pumping water around the country and treating our sewage is about 0.4 kWh per day per person.
Figure 15.8: Energy requirements of different forms of freight-transport. The vertical coordinate shows the energy consumed in kWh per net ton-km, (that is, the energy per t-km of freight moved, not including the weight of the vehicle). See also figure 20.23 (energy requirements of passenger transport).
Water transport requires energy because boats make waves. Nevertheless, transporting freight by ship is surprisingly energy efficient.
At the moment the UK doesn’t spend energy on water desalination. But there’s talk of creating desalination plants in London. What’s the energy cost of turning salt water into drinking water? The least energy-intensive method is reverse osmosis. Take a membrane that lets through only water, put salt water on one side of it, and pressurize the salt water. Water reluctantly oozes through the membrane, producing purer water – reluctantly, because pure water separated from salt has low entropy, and nature prefers high entropy states where everything is mixed up. We must pay high-grade energy to achieve unmixing.
Figure 15.9: Water delivery: 0.3 kWh/d; sewage processing: 0.1 kWh/d.
The Island of Jersey has a desalination plant that can produce of pure water per day (figure 15.10). Including the pumps for bringing the water up from the sea and through a series of filters, the whole plant uses a power of 2 MW. That’s an energy cost of of water produced. At a cost of 8 kWh per , a daily water consumption of 160 litres would require 1.3 kWh per day.
Figure 15.10: Part of the reverse-osmosis facility at Jersey Water’s desalination plant. The pump in the foreground, right, has a power of 355 kW and shoves seawater at a pressure of 65 bar into 39 spiral-wound membranes in the banks of blue horizontal tubes, left, delivering per day of clean water. The clean water from this facility has a total energy cost of 8 kWh per .
Supermarkets in the UK consume about 11 TWh of energy per year. Shared out equally between 60 million happy shoppers, that’s a power of 0.5 kWh per day per person.
The significance of imported stuff
In standard accounts of “Britain’s energy consumption” or “Britain’s carbon footprint,” imported goods are not counted. Britain used to make its own gizmos, and our per-capita footprint in 1910 was as big as America’s is today. Now Britain doesn’t manufacture so much (so our energy consumption and carbon emissions have dropped a bit), but we still love gizmos, and we get them made for us by other countries. Should we ignore the energy cost of making the gizmo, because it’s imported? I don’t think so. Dieter Helm and his colleagues in Oxford estimate that under a correct account, allowing for imports and exports, Britain’s carbon footprint is nearly doubled from the official “11 tons per person” to about 21 tons. This implies that the biggest item in the average British person’s energy footprint is the energy cost of making imported stuff.
In Chapter Stuff II, I explore this idea further, by looking at the weight of Britain’s imports. Leaving aside our imports of fuels, we import a little over 2 tons per person of stuff every year, of which about 1.3 tons per person are processed and manufactured stuff like vehicles, machinery, white goods, and electrical and electronic equipment. That’s about 4 kg per day per person of processed stuff. Such goods are mainly made of materials whose production required at least 10 kWh of energy per kg of stuff. I thus estimate that this pile of cars, fridges, microwaves, computers, photocopiers and televisions has an embodied energy of at least 40 kWh per day per person.
To summarize all these forms of stuff and stuff-transport, I will put on the consumption stack 48 kWh per day per person for the making of stuff (made up of at least 40 for imports, 2 for a daily newspaper, 2 for road- making, 1 for house-making, and 3 for packaging); and another 12 kWh per day per person for the transport of the stuff by sea, by road, and by pipe, and the storing of food in supermarkets.
Work till you shop.
Notes and further reading
One aluminium drinks can costs 0.6 kWh. The mass of one can is 15 g. Estimates of the total energy cost of aluminium manufacture vary from 60 MJ/kg to 300 MJ/kg. [yx7zm4], [r22oz], [yhrest]. The figure I used is from The Aluminum Association [y5as53]: 150 MJ per kg of aluminium (40 kWh/kg).
The embodied energy of a water bottle made of PET. Source: Hammond and Jones (2006) – PET’s embodied energy is 30 kWh per kg.
The average Brit throws away 400 g of packaging per day. In 1995, Britain used 137 kg of packaging per person (Hird et al., 1999).
A personal computer costs 1800 kWh of energy. Manufacture of a PC requires (in energy and raw materials) the equivalent of about 11 times its own weight of fossil fuels. Fridges require 1–2 times their weight. Cars require 1–2 times their weight. Williams (2004); Kuehr (2003).
...a rechargeable nickel-cadmium battery. Source: Rydh and Karlström(2002).
...steel... From Swedish Steel, “The consumption of coal and coke is 700 kg per ton of finished steel, equal to approximately 5320 kWh per ton of finished steel. The consumption of oil, LPG and electrical power is 710 kWh per ton finished product. Total [primary] energy consumption is thus approx. 6000 kWh per ton finished steel.” (6 kWh per kg.) [y2ktgg]
A new car’s embodied energy is 76000 kWh. Source: Treloar et al. (2004). Burnham et al. (2007) give a lower figure: 30 500 kWh for the net life-cycle energy cost of a car. One reason for the difference may be that the latter life-cycle analysis assumes the vehicle is recycled, thus reducing the net materials cost.
Figure 15.11: Making our stuff costs at least 48 kWh/d. Delivering the stuff costs 12 kWh/d.
Paper has an embodied energy of 10 kWh per kg. Making newspaper from virgin wood has an energy cost of about 5 kWh/kg, and the paper itself has an energy content similar to that of wood, about 5 kWh/kg. (Source: Ucuncu (1993); Erdincler and Vesilind (1993).) Energy costs vary between mills and between countries. 5 kWh/kg is the figure for a Swedish newspaper mill in 1973 from Norrström (1980), who estimated that efficiency measures could reduce the cost to about 3.2 kWh/kg. A more recent full life-cycle analysis (Denison, 1997) estimates the net energy cost of production of newsprint in the USA from virgin wood followed by a typical mix of landfilling and incineration to be 12 kWh/kg; the energy cost of producing newsprint from recycled material and recycling it is 6 kWh/kg.
The energy intensity of road transport in the UK is about 1 kWh per t-km. Source: www.dft.gov.uk/pgr/statistics/datatablespublications/energyenvironment.
The energy intensity of freight transport by this container ship is 0.015 kWh per ton-km. The Ever Uberty – length 285m, breadth 40m – has a capacity of 4948 TEUs, deadweight 63000 t, and a service speed of 25 knots; its engine’s normal delivered power is 44 MW. One TEU is the size of a small 20-foot container – about . Most containers you see today are 40-foot containers with a size of 2 TEU. A 40-foot container weighs 4 tons and can carry 26 tons of stuff. Assuming its engine is 50%-efficient, this ship’s energy consumption works out to 0.015 kWh of chemical energy per ton-km. www.mhi.co.jp/en/products/detail/container_ship_ever_uberty.html
– Britain’s share of international shipping... Source: Anderson et al. (2006).
Figure 15.8. Energy consumptions of ships. The five points in the figure are a container ship (46 km/h), a dry cargo vessel (24 km/h), an oil tanker (29 km/h), an inland marine ship (24 km/h), and the NS Savannah (39 km/h).
Dry cargo vessel 0.08 kWh/t-km. A vessel with a grain capacity of carries 3360 deadweight tons. (Dead-weight tonnage is the mass of cargo that the ship can carry.) It travels at speed 13 kn (24 km/h); its one engine with 2 MW delivered power consumes 186 g of fuel-oil per kWh of delivered energy (42% efficiency). conoship.com/uk/vessels/detailed/page7.htm
Oil tanker A modern oil tanker uses 0.017 kWh/t-km [6lbrab]. Cargo weight 40000 t. Capacity: . Main engine: 11.2 MW maximum delivered power. Speed at 8.2 MW: 15.5 kn (29 km/h). The energy contained in the oil cargo is 520 million kWh. So 1% of the energy in the oil is used in transporting the oil one-quarter of the way round the earth (10000 km).
Roll-on, roll-off carriers The ships of Wilh. Wilhelmsen shipping company deliver freight-transport with an energy cost between 0.028 and 0.05 kWh/t-km [5ctx4k].
Water delivery and sewage treatment costs 0.4 kWh/d per person. The total energy use of the water industry in 2005–6 was 7703 GWh. Supplying 1 of water has an energy cost of 0.59 kWh. Treating of sewage has an energy cost of 0.63 kWh. For anyone interested in greenhouse-gas emissions, water supply has a footprint of 289 g per of water delivered, and wastewater treatment, 406 g per of wastewater.
Domestic water consumption is 151 litres per day per person. Total water consumption is 221 l/d per person. Leakage amounts to 57 litres per day per person. Sources: Parliamentary Office of Science and Technology [www.parliament.uk/documents/upload/postpn282.pdf], Water UK (2006).
Supermarkets in the UK consume 11 TWh/y. [yqbzl3]
Helm et al. suggest that, allowing for imports and exports, Britain’s carbon footprint is nearly doubled to about 21 tons. Helm et al. (2007).