Environmental accounts show how the environment contributes to the economy (for example, through the extraction of raw materials), the impacts that the economy has on the environment (for example, energy consumption and air emissions), and how society responds to environmental issues (for example, through taxation and expenditure on environmental protection).
Environmental accounts are ‘satellite accounts’ to the main National Accounts and they are compiled in accordance with the System of Environmental Economic Accounting (SEEA), which closely follows the UN System of National Accounts (SNA). This means that they are comparable with economic indicators such as Gross Domestic Product (GDP).
Environmental accounts are used nationally and internationally, primarily by governments, development organisations and researchers, to inform sustainable development policy, to evaluate the environmental impacts of different sectors of the economy, and to model impacts of fiscal or monetary measures.
In this release
The environmental accounts included in this release have been divided into the following categories:
Natural capital accounts:
Oil and gas reserves
Physical flow accounts:
Fuel use and energy consumption
Environmental protection expenditure
Experimental natural capital accounts
There is also a ‘Revisions’ section that details improvements that have been made since UK Environmental Accounts, 2013 was published last year.
Figures 1 and 2 show changes in mean air temperature and Gross Domestic Product (GDP) from 1990 to 2013. These measures help to contextualise some of the changes observed across the environmental accounts. For example, the average temperature fell in 2010 to 8.0°C from 9.2°C in 2009, which contributed to the increases in energy consumption and greenhouse gas emissions observed during that year. At the same time, GDP started to recover following the economic downturn, which may also explain the increases in energy consumption and emissions.
The relationships between the environment and the economy are explored further throughout this bulletin.
The following presents non-monetary analysis of the UK’s oil and gas discovered reserves and undiscovered resources. Discovered reserves refer to estimates of oil and gas that are expected to be technically and commercially producible. On the other hand, undiscovered resources refer to estimates of potentially recoverable oil and gas resources that have not yet been discovered.
Estimates of oil and gas reserves and resources are prepared and published annually by the Department of Energy & Climate Change (DECC).
Oil is defined in the estimates as both oil and the liquids that can be obtained from gas fields. Shale oil is not included in these estimates.
At the end of 2012, the upper range of total oil reserves and resources was 2,406 million tonnes (mt). This is calculated as the sum of discovered reserves and the upper estimate of undiscovered resources. This figure is down 0.9%, or 21 mt, compared with 2011. Also in 2012, the lower range of total oil reserves and resources increased to 860 mt, up by 3.0%, from 835 mt in 2011.
Oil reserves are split into three categories. Proven reserves have a 90% chance or greater of being technically and commercially producible. Probable reserves are not yet proven, but have a greater than 50% chance of being technically and commercially producible. Possible reserves have a chance of being produced, but at a probability of less than 50%.
The expected level of reserves is the sum of proven and probable reserves. In 2012, this was equal to 811 mt, an increase of 2.9% from 788 mt in 2011. Extraction of oil during 2012 was estimated to be 45 mt, down 13.5% from 52 mt in 2011. Comparing 2012 to 2011:
Proven reserves fell 1.9% to 405 mt. Although extraction was 45 mt in 2012, there was a net transfer of 37 mt from probable reserves to proven reserves, due to development approval of 12 new oil fields being granted.
Probable reserves rose by 8.3% to 405 mt.
Possible oil reserves decreased by 66 mt to 253 mt, a fall of 20.7%. The majority of this fall was due to the reallocation of possible reserves to probable reserves, as well as downward revisions to possible reserves.
The maximum level of discovered oil reserves that could be recovered are the sum of proven, probable and possible reserves. This was equal to 1,064 mt in 2012, down by 3.8% from 1,106 mt in 2011.
Estimates of undiscovered resources are split by a lower range and an upper range. Undiscovered estimates provide a broad indication of potential oil resources that could be extracted in the future.
In 2012, the lower range estimate of undiscovered oil resources was 455 mt, an increase of 7.8% compared to 2011. The upper range estimates of undiscovered oil resources also increased to 1,342 mt, or 1.6%, from 1,321 mt in 2011.
The increase in undiscovered oil resources is due to the addition of new extraction prospects discovered with the granting of further offshore licenses in 2012. Some existing prospects were re-assessed, reducing the overall increase in undiscovered oil resources.
Gas is defined as gas expected to be available for sale from dry gas fields, gas condensate fields, oil fields with associated gas, and a small amount from coal bed methane projects. Shale gas is not included in these estimates.
In 2012, the upper range of total gas reserves and resources was 1,709 billion cubic metres (bcm). This is calculated as the sum of discovered reserves and the upper estimate of undiscovered resources. This is an increase of 1.4%, or 23 bcm compared with 2011. Also in 2012, the lower range of total gas reserves and resources increased to 613 bcm, up by 2.3% from 599 bcm in 2011.
As with oil, gas reserves are split into three categories: proven, probable, and possible reserves.
The expected level of reserves is equal to proven plus probable gas reserves. In 2012, this was estimated to be 461 bcm, down 6.5% from 493 bcm in 2011. Extraction of gas in 2012 was 37 bcm, decreasing from 43 bcm in 2011. Further, comparing 2012 against 2011:
The level of proven gas reserves fell by 0.8% to 244 bcm in 2012. During 2012, development approval was granted for nine offshore gas fields, increasing the level of proven reserves, as a result, 35 bcm was transferred from probable to proven reserves. This largely offset the extraction of 37 bcm.
The level of probable gas reserves fell to 217 bcm at the end of 2012, a decrease of 11.8% compared to 2011. Although there was a small allocation from possible to probable reserves, this was not as high as the reallocation of reserves from probable to proven.
Possible gas reserves increased 10.2% to 238 bcm in 2012, an increase from 216 bcm in 2011.
The maximum level of discovered gas reserves that could be recovered equals proven, probable and possible reserves. This was equal to 699 bcm in 2012, down from 709 bcm in 2011.
As with undiscovered oil resources, estimates of undiscovered gas resources are split by a lower range and an upper range. Undiscovered estimates provide a broad indication of potential gas resources that could be extracted in the future.
At the end of 2012, the lower range estimates of undiscovered gas resources was 369 bcm, an increase of 16 bcm from 2011 (or 4.5%). The upper range estimates of undiscovered gas resources increased by 3.4% to 1,010 bcm compared with 2011. As with oil, the increase in undiscovered gas resources is due to the addition of new extraction prospects discovered with the granting of further offshore licenses in 2012. Some existing prospects were re-assessed, reducing the overall increase in undiscovered gas resources.
Estimates of undiscovered resources must be treated with caution. They provide only a broad indication of the ultimate remaining potential resources. The limits of these ranges should not be regarded as minima or maxima or implying any particular level of probability.
Since 2011, ONS has been developing methodology to estimate the monetary value of UK Continental Shelf (UKCS) oil and gas reserves. The latest methodology and estimates can be found on the Environmental Accounts: Natural resources methodology pages on the ONS website.
A fuel is a combustible material and when burned it can produce energy. Total fuel use differs from energy consumption as some fuels are consumed for non-energy purposes, such as to produce chemicals or other fuels. In addition, energy consumption includes other sources of energy that are not combustible (nuclear, imports, primary renewable electricity) and therefore the energy inputs have no calorific value; as a result these are not included here within fuel use. For the purposes of this publication, ‘Fuel use’ is defined also to exclude combustible renewable and waste fuels.
The methodology of the fuel use accounts are based on a UK ‘residency’ basis (as opposed to a ‘territorial’ basis) in line with the National Accounts, which includes fuel use by UK resident persons and businesses visiting other countries, but exclude fuel use caused by visiting foreign persons and businesses in the UK.
Fuel use increased slightly between 2011 and 2012 by 0.8%, in contrast to the overall declining trend since 2004, largely as a result of cooler air temperatures demanding greater fuel consumption.
In 2012, coal use increased by 24.3% whilst natural gas use continued to decline, reflecting the recent price increase of gas relative to coal.
Total fuel use in 2012 was 194.1 Mtoe, an increase of 0.8% from 2011, when total fuel use reached its lowest since the series began in 1990 (Figure 7). Fuel use in 2012 was 19.1 Mtoe (9.0%) lower than in 1990 and 15.8% lower than its peak in 2004 at 230.5 Mtoe. Since 2004, fuel use has been on a downward trend as a result of a move towards more efficient use of fuel and alternative sources of energy that are renewable and sustainable. A few exceptions to this trend occurred in 2010 and again in 2012 when cooler temperatures demanded more fuel usage for energy consumption.
Since 1993 natural gas has been the most used fuel, increasing from 59.9 Mtoe in 1993 to 96.2 Mtoe in 2004, after which total fuel use began to follow a general declining trend, and in 2012 natural gas use was 72.4 Mtoe (Figure 8), comprising 37.3% of total fuels.
Consumption of other types of fuel in Figure 8 have also been declining since about 2004, apart from DERV (road-diesel), which gradually increased to 23.9 Mtoe in 2012. In contrast, petrol use declined by 32.2% between 2004 and 2012, which may indicate a switch to more fuel efficient fuels for on-road use.
Between 2011 and 2012, coal use increased the greatest, from 32.9 Mtoe to 41.0 Mtoe, a 24.3% increase and accounting for 21.1% of total fuel use in 2012. Coal use has generally declined since 1990, the reason for the increase in 2012 may reflect a change from natural gas use, which declined by 5.5% between 2011 and 2012, to cheaper coal use.
Generally, the other fuels1 have been declining since the series began from 56.5 Mtoe in 1990 to 41.9 Mtoe in 2012, a 25.8% decrease. On closer inspection of the other fuels, use of aviation fuels has been increasing whilst usage of the other contributing fuels declined.
For more detailed fuel use data see the
Fuel use by type (130.5 Kb Excel sheet)
Fuel use by industry, source and fuel type (599.5 Kb Excel sheet)
Energy consumption is the use of energy for power generation, heating and transport. Energy is essential to all economic activities, for example, as input for production processes and as a consumer commodity.
In this release, ‘direct use of energy’ refers to the energy content of consumed fuel in its original state, before any transformation to other forms of energy occurs, allocated to the original purchasers and consumers of fuels. Whereas, for ‘reallocated use of energy’ the losses incurred during transformation1 and distribution2 are allocated to the final consumer of the energy rather than incorporating it all in the electricity generation sector.
The methodology of the energy accounts are based on a UK ‘residency’ basis (as opposed to a ‘territorial’ basis) in line with the National Accounts, which includes energy consumed by UK resident persons and businesses visiting other countries, but excludes energy consumption by visiting foreign persons and businesses in the UK.
Total energy consumption increased by 1.2% from 2011 to 2012, contrary to the general declining trend since 2005, largely due to average air temperatures being 1 degree Celsius lower in 2012.
Between 2011 and 2012, energy consumption from renewable and waste sources increased by 11.1%, increasing from 8.7 to 9.6 Million tonnes of oil equivalent (Mtoe) and contributing 4.5% of total energy consumption.
The rate at which energy intensity has declined has slowed-down since 2007, thought to reflect the downturn in the economy.
In 2012, total energy consumption of primary fuels and equivalents was 214.8 Mtoe, 1.2% higher consumption than in 2011 (212.2 Mtoe) (Figure 9). Energy consumption, particularly by households, is closely related to air temperature (DECC, 2013a). The growth observed in 2012 was mainly driven by colder weather compared to that experienced in 2011, with average air temperature being 1 degree Celsius lower (DECC, 2013b).
Since 2005, the general trend of total energy consumption of primary fuels and equivalents has declined. Deviations from this trend occurred in 2010 and 2012, with a 2.9% and 1.2% increase of total energy consumed on the previous year, respectively (Figure 9). The large excursion observed in 2010 reflects the particularly cold weather experienced that year.
The decline in total energy consumption of primary fuels and equivalents since 2005 (Figure 9), is also reflected in the decline of energy consumption from fossil fuels (Figure 10). In 2008 energy consumption from fossil fuels dramatically declined, however from 2009 a gradual increase in energy consumption from other sources occurred, particularly in nuclear, renewables and waste sources (Figure 10). A peak in fossil fuel consumption in 2010 may reflect the colder weather of 2010 resulting in increased consumption by ‘households’. At the same time a slight decline in energy from other sources was observed. In 2012, direct use of energy from fossil fuels was 189.0 Mtoe, an increase of 0.9% on the year before. Energy from other sources (imports, nuclear, renewables and waste sources) also increased from 24.8 Mtoe to 25.9 Mtoe, a 4.4% increase compared to 2011.
The energy consumption of primary fuels and equivalents is reallocated3 by final consumer industry sector. In 2012, the ‘household’4 sector used the largest proportion of the energy consumed at 37.2% (79.9 Mtoe), with ‘manufacturing’ (45.7 Mtoe), ‘transport and storage; information and communication’ (32.3 Mtoe), ‘wholesale and retail trade; repair of motor vehicles’ (11.9 Mtoe) sectors using a further 41.9% (Figure 11).
For more detailed energy data see: Energy consumption (164.5 Kb Excel sheet) , Energy use and intensity by industry, (242.5 Kb Excel sheet) and Energy by industry, source and fuel (1.55 Mb Excel sheet) .
Environmental Accounts estimates follow the UN System of Environmental Economic Accounts (SEEA) framework which is an internationally agreed standard5.
They are not reported on the same basis as published by the Department of Energy & Climate Change (DECC) in the Digest of UK Energy Statistics (DUKES) which follow Eurostat, and IEA guidelines and the United Nations International Recommendations for Energy Statistics. The National Accounts measure includes energy consumed by UK companies and households abroad and excludes energy consumption by foreign residents in the UK as well as further differences in definition. As a result of this and other differences the DUKES measure for UK energy consumption is 0.9 Mtoe lower than the environmental accounts measure in 2012.
The Energy bridging table (195.5 Kb Excel sheet) shows the differences between the two estimates. Further information about the relationship between environmental accounts measures and those released by DECC is available in an energy bridging table and methodology article.
In 2012, 9.6 Mtoe of energy was consumed from renewable and waste sources (Figure 10), contributing 4.5% of total energy consumption.
Energy consumption from renewable and waste sources in 2012 was 7.1 times greater than in 1990, when the time series began. In 2004, and again in 2007, energy consumption from renewable and waste sources rapidly increased. Between 2011 and 2012, an 11.1% increase was observed, from 8.7 to 9.6 Mtoe.
In 2012, 38.7% (3.7 Mtoe) of energy consumed from renewable and waste sources came from waste6, 23.3% (2.2 Mtoe) from renewable generation7, 20.2% (1.9 Mtoe) from wood and straw8 and 17.8% (1.7 Mtoe) from biofuels9 (Figure 12).
Since 1996, energy consumption from waste sources has increased by 331.5% from 0.9 Mtoe to 3.7 Mtoe (Figure 13), predominately due to a rise in energy consumption from landfill gas and municipal solid waste (MSW). The greatest increase of energy consumption from waste sources occurred between 2011 and 2012, from 3.3 to 3.7 Mtoe due to a 32.5% increase in energy consumption from MSW. Energy consumption from renewable generation, wood and straw and biofuels energy notably increased from about 2004 onwards, largely as a result of increases in energy consumption from wind energy, wood, and road-transport biofuels, respectively.
Since the time series began in 1990, the largest consumers of renewable and waste energy have been ‘households’4, ‘energy supply, water, and waste’ industries, and the ‘manufacturing’ sector (Figure 14). Since 2004, ‘households’ have been the largest consumers, rising from 1.2 Mtoe to 3.1 Mtoe in 2012, an overall increase of 162.0% and accounting for 32.0% of energy consumed from renewable and waste sources in 2012. The rise in energy consumption of renewable and waste sources by ‘households’ since 2004 is primarily due to an increase in biofuel usage in road transport and consumption of renewable primary electricity (particularly wind, wave and tidal energy).
The ‘energy supply, water, and waste sector’ was the second largest consumer of energy from renewable and waste sources, with 22.0% consumed (2.1 Mtoe) in 2012. A sharp increase in 2004 and a rise in 2008 represent increased combustion of MSW. In 2012, the ‘manufacturing’ sector was the third largest consumer, using 2.1 Mtoe and accounting for 21.9% of energy from renewable and waste sources. A peak in energy consumption from renewable and waste sources in the ‘manufacturing’ sector in 2003 reflects a rise in biomass production in industrial plants that year. Many of the other sectors have increased their consumption of energy from renewable and waste resources, particularly since 2004 onwards, largely from landfill gas, MSW, wood, biofuels, and renewable primary electricity.
Energy intensity1, energy use per unit of value added (constant price level), can be an indicator of the energy efficiency of the economy. A reduction in energy intensity may indicate a more efficient use of energy in production process but it may also reflect changes to the structure of the economy, for example, a change from manufacturing industries to services.
Since 1997, when the time series began, energy intensity of the UK economy, excluding consumer expenditure, has been following a downward trend from 6.1 TJ/£m in 1997 to 4.2 TJ/£m in 2012; a 31.0% decrease in energy intensity (Figure 15). Between 2000 and 2001, and again in 2009 to 2010, energy intensity plateaued at 5.7 and 4.4 TJ/£m, respectively. This was due to an increase in energy use relative to GVA in 2001 and in 2010, likely driven by lower average annual air temperatures in those years. Since 2007, the rate at which energy intensity has decreased has slowed down; this is thought to reflect the impact of the recent financial crisis on the economy.
Energy intensity across most industrial sectors has remained fairly constant since 2007, although the ‘manufacturing’ and ‘transport and storage; information and communication’ sectors showing a notable decline. This is likely due to a combination of energy efficiency improvements in production processes and transport, and also a decline in activity of more energy intensive industries such as cement, iron and steel. Since 2007, the ‘mining and quarrying’ industry has shown a large increase in energy intensity of 28.3% due to a decline in value added from this sector.
Some of the largest increases in energy intensity between 2011 and 2012 were in the ‘construction’, ‘mining and quarrying’, and ‘agriculture, forestry and fishing’ sectors (Figure 16), due to GVA falling faster than energy consumption. ‘Energy supply, water, and waste’, ‘financial and insurance activities’ and the ‘arts, entertainment and recreation; other service activities’ also experienced increases in energy intensity but as a result of rises in energy consumption relative to GVA. In contrast, ‘activities of households as employers’ experienced a decline in energy intensity due to an increase in GVA. ‘Transport and storage; information and communication’, and ‘manufacturing’ industries also saw a decline in energy intensity between 2011 and 2012 but as a result of falling energy consumption relative to GVA. This could be due to a drop in production levels requiring less energy.
For more detailed energy intensity data see: Energy use and intensity by industry (242.5 Kb Excel sheet) .
Atmospheric (air) emissions show the physical flow of gaseous or particulate materials from the national economy (through production or consumption processes) to the atmosphere. Air emissions data included in this release are based on a UK ‘residency’ basis (as opposed to a ‘territorial’ basis)1, which includes emissions that UK resident persons and businesses are directly responsible for in other countries (dominated by emissions related to travel and transport overseas), but exclude emissions caused by visiting foreign persons and businesses in the UK. The main use of air emissions accounts is to inform sustainable development policy and to evaluate the environmental impact of different industries.
Greenhouse gas emissions have generally decreased since the mid-1990s, falling from a peak of 822.9 million tonnes of CO2 equivalent (CO2e) in 1991 to 642.0 million tonnes of CO2e in 2011, the lowest point in the series.
In 2012, greenhouse gas emissions increased by 2.2% to 656.3 million tonnes of CO2e.
Over the past two decades, acid rain precursor (ARP) emissions have decreased sharply, falling by 70.5% from 6.9 million tonnes of SO2 equivalent (SO2e) in 1990 to 2.0 million tonnes of SO2e in 2012.
Air emissions are divided into greenhouse gas emissions, acid rain precursors, heavy metal pollutants, and other pollutants. Emissions related to fuel sources used by road transport are also included.
Atmospheric emissions of greenhouse gases are widely believed to contribute to global warming and climate change. They include:
Carbon dioxide (CO2),
Nitrous oxide (N2O),
Perfluorocarbons (PFC), and
Sulphur hexafluoride (SF6).
The potential of each greenhouse gas to cause global warming is assessed in relation to a given weight of carbon dioxide. Consequently, all greenhouse gas emissions are measured as CO2 equivalents (CO2e).
Since the mid-1990s, greenhouse gas emissions have generally decreased, falling from a peak of 822.9 million tonnes of CO2e in 1991 to 642.0 million tonnes of CO2e in 2011, the lowest point in the series. This was primarily due to decreases within the ‘manufacturing’ and ‘energy supply, water and waste’ sectors. The greatest fall occurred in 2009 following the start of the economic recession in 2008, when emissions decreased by 7.8% from 718.7 to 662.3 million tonnes of CO2e.
In 2012, greenhouse gas emissions increased by 2.2% from 2011 to 656.3 million tonnes of CO2e. This consisted of:
555.4 million tonnes (84.6%) of carbon dioxide,
50.4 million tonnes (7.7%) of methane (CO2e),
35.8 million tonnes (5.4%) of nitrous oxide (CO2e),
13.9 million tonnes (2.1%) of hydro-fluorocarbons (CO2e), and
0.8 million tonnes (0.1%) of other greenhouse gases (CO2e).
On average, carbon dioxide emissions represented approximately four-fifths (81.3%) of total greenhouse gas emissions between 1990 and 2012. Methane emissions represented 10.2%, nitrous oxide represented 6.6% and other greenhouse gases represented 1.9%.
Compared with 1990, Figure 17 shows that emissions of all greenhouse gases (apart from hydro-fluorocarbons) were lower in 2012. The main reasons for the reductions are:
The 11.5% fall in carbon dioxide emissions was primarily due to a 35.5% decrease in the manufacturing sector, caused mainly by a large decline in emissions from fuel-oil combustion.
The 51.5% decline in methane emissions was largely caused by a 54.7% reduction in the ‘energy supply, water and waste’ sectors, driven by a large decrease in emissions from landfill.
The 48.3% fall in nitrous oxide emissions was due mainly to a 97.3% fall in the manufacturing sector, which was largely due to the cessation of industrial adipic acid production in the UK during 2009.
Figure 18 shows that the ‘energy supply, water and waste’ sectors emitted the greatest amount of greenhouse gases in 2012 (203.1 million tonnes of CO2e). There was an 8.7% increase in CO2 emissions in this sector in 2012 to 176.2 million tonnes from 162.1 million tonnes in 2011, which was primarily caused by an increase in emissions from coal use in power stations. However, at the same time, methane emissions in this sector fell by 4.3% from 25.1 million tonnes of CO2e in 2011 to 24.0 million tonnes of CO2e in 2012, which was mainly due to a decrease in emissions from landfill.
Consumer expenditure accounted for the second highest amount of greenhouse gas emissions in 2012 at 141.7 million tonnes of CO2e, of which 136.1 million tonnes (96.1%) were carbon dioxide emissions. This includes emissions caused by household expenditure on fuel.
Greenhouse gas emissions data by economic sector are available in the Atmospheric emissions: Greenhouse gas emissions (439 Kb Excel sheet) dataset.
Acid rain can have harmful effects on the environment and is caused primarily by emissions of sulphur dioxide (SO2), nitrogen oxide (NOX) and ammonia (NH3). For comparability, all figures are presented as sulphur dioxide equivalents (SO2e).
Over the past two decades, acid rain precursor (ARP) emissions (excluding natural world) have decreased sharply, falling by 70.5% from 6.9 million tonnes of SO2e in 1990 to 2.0 million tonnes of SO2e in 2012. ARP emissions have remained stable at approximately 2.1 million tonnes of SO2e each year since 2009.
Sulphur dioxide emissions were 86.3% lower in 2012 compared with 1990. This was largely due to decreases in emissions from coal use in power stations within the ‘energy supply, water and waste’ sectors. However, sulphur dioxide emissions increased by 6.0% in 2012 to 547.1 thousand tonnes of SO2e from 516.2 thousand tonnes of SO2e in 2011.
Emissions of nitrogen oxide declined by 58.0% between 1990 and 2012, which was primarily due to a large decrease in emissions from petrol use in cars. In 2012, nitrogen oxide emissions reduced by 4.3% from 996.9 thousand tonnes of SO2e in 2011 to 954.4 thousand tonnes of SO2e.
Ammonia emissions fell by 17.5% between 1990 and 2012, which was due in part to a decrease in emissions from agricultural soils in the ‘agriculture, forestry and fishing’ sector. Emissions increased slightly in 2009, 2010 and 2011, but fell to 530.9 thousand tonnes of SO2e in 2012.
Acid rain precursor emissions data by economic sector are available in the Atmospheric emissions: Acid rain precursor emissions (302 Kb Excel sheet) dataset.
Emissions of heavy metal pollutants can affect air quality and health. Table 1 shows emissions of heavy metal pollutants in 1990 and 2012.
Emissions of all heavy metal pollutants declined between 1990 and 2012. The most notable reduction was in emissions of lead, which fell by 97.9% from 3,053.4 tonnes in 1990 to 63.5 tonnes in 2012. This was mostly due to the decrease in the use of leaded petrol, the marketing of which was prohibited within the EU from 2000.
Emissions of heavy metal pollutants data by economic sector are available in the Atmostpheric emissions: Heavy metal pollutant emissions (846 Kb Excel sheet) dataset.
There are a number of other pollutants that affect air quality. Table 2 shows emissions of other pollutants in 1990 and 2012.
|Non-methane volatile organic compound||2,870.5||912.2|
Carbon monoxide (CO) emissions were 77.8% lower in 2012 compared with 1990. During the same period, emissions of non-methane volatile organic compound (NMVOC) fell by 68.2%. These decreases were mainly due to reductions in road transport emissions, which fell by 89.8% for CO and 95.8% for NMVOC over the period. This is a result of a large switch from petrol to diesel cars, as petrol engines emit more CO and NMVOC than diesel engines.
Airborne Particulate Matter (PM) consists of solid and/or liquid materials that are generated from both manmade and natural sources. PM10 and PM2 . 5 emissions decreased by 55.0% and 58.1% respectively between 1990 and 2012. Residential and industrial coal combustion had been a major source of PM emissions in the UK. However, the Clean Air Act 1993 restricted coal combustion and this accounts for reductions in emissions across many sectors.
Emissions of other pollutants data by economic sector are available in the
Atmospheric emissions: Emissions of other pollutants (567.5 Kb Excel sheet)
Various pollutants are emitted from road transport into the atmosphere. Figure 20 shows greenhouse gas emissions generated from fuel sources used by road vehicles from 1990 to 2012.
Greenhouse gas emissions related to road transport generally increased from the early 1990s until 2007. However, since 2008 emissions have declined, which in part reflects the economic downturn and an increase in more energy efficient vehicles.
In 2012, road transport emissions accounted for 17.2% (112.7 million tonnes of CO2e) of total greenhouse gas emissions (656.3 million tonnes of CO2e). This consisted of:
111.8 million tonnes of CO2,
0.05 million tonnes (CO2e) of methane, and
0.9 million tonnes (CO2e) of nitrous oxide.
Road transport emissions of acid raid precursors decreased by 73.1% between 1990 and 2012 from 932.6 to 250.6 thousand tonnes of SO2e respectively.
PM emissions related to road transport peaked in 1996 and then continuously decreased to their lowest levels in 2012, at 22.8 thousand tonnes for PM10 and 16.2 thousand tonnes for PM2 .5. Diesel engine vehicles emit a greater mass of PM per kilometre than petrol engine vehicles. Since 1992, diesel vehicles have had to meet tighter PM emission regulations. This has led to reductions in PM emissions, despite the use of diesel vehicles increasing.
More detailed road transport emissions data are available in the Atmospheric emissions: Road transport emissions (116.5 Kb Excel sheet) dataset.
Estimates within Environmental Accounts are produced in accordance with the UN System of Environmental-Economic Accounting (SEEA), which is an internationally agreed standard. UK Environmental Accounts are reported on a UK ‘residency’ basis, which include emissions that UK resident persons and businesses are directly responsible for in other countries (dominated by travel and transport overseas), but exclude emissions caused by visiting foreign persons and businesses in the UK. This is consistent with UK National Accounts and enables comparison with economic indicators such as Gross Domestic Product (GDP).
UK air emissions estimates that are reported internationally to the United Nations Framework Convention on Climate Change (UNFCCC) and the United Nations Economic Commission for Europe (UNECE) are reported on a ‘territory’ basis, which only include emissions that occur within the UK’s territorial boundaries.
Tables that illustrates the differences between UK Environmental Accounts estimates and UNFCCC and UNECE estimates can be found in the
Emissions bridging table (321.5 Kb Excel sheet)
Greenhouse gas emissions intensity measures the level of emissions per unit of economic output.1 It can be used to examine the relationship between economic growth and greenhouse gas emissions, a measure of sustainability.
Greenhouse gas emissions intensity was 37.7% lower in 2012 (0.38 thousand tonnes of CO2e per £ million) compared with 1997 (0.61 thousand tonnes of CO2e per £ million).
Emissions intensity is greatest in the ‘agriculture, forestry and fishing’ and ‘energy supply, water and waste’ sectors.
Figure 21 shows that greenhouse gas emissions intensity has followed a downward trend since the series began, declining by 37.7% between 1997 (0.61 thousand tonnes of CO2e per £ million value added) and 2012 (0.38 thousand tonnes of CO2e per £ million value added). Although economic output (Gross Value Added (GVA)) has generally increased, greenhouse gas emissions have generally decreased, which has led to the falls in emissions intensity.
Greenhouse gas emissions intensity is greatest in the ‘agriculture, forestry and fishing’ and ‘energy supply, water and waste’ sectors. Figure 22 shows that intensity levels in these sectors were lower in 2012 compared with 1997, although there were increases in both between 2011 and 2012: emissions intensity increased from 5.91 to 6.07 thousand tonnes CO2e per £million (2.71%) in the ‘agriculture, forestry and fishing’ industry and from 5.76 to 6.18 thousand tonnes CO2e per £million (7.29%) in the ‘energy supply, water and waste’ industries.
Compared with 1997, greenhouse gas emissions intensity was higher in 2012 in only three sectors:
‘Mining and quarrying’ (0.75 to 0.86 thousand tonnes CO2e per £million),
‘Wholesale and retail trade; repair of motor vehicles and motorcycles’ (0.11 to 0.12 thousand tonnes CO2e per £million), and
‘Households as employers’ (0.03 to 0.04 thousand tonnes CO2e per £million).
More detailed greenhouse gas emissions intensity data are available in the
Atmospheric emissions: Greenhouse gas emissions intensity (125 Kb Excel sheet)
Material flow accounts show the quantity of raw materials extracted within the UK (domestic extraction), as well as the imports and exports of these items in their raw, semi-manufactured and finished product forms. This information is used to calculate indicators showing the quantity of materials that are available for use and that are consumed within the economy.
Extraction of raw materials in the UK has continually declined since 2000, reaching 460.3 million metric tonnes in 2012.
The decline in extraction has been partly offset in recent years by a rise in physical imports (to 286.8 million tonnes in 2012) and a fall in exports (to 157.0 million tonnes in 2012).
The total amount of materials available for use (Direct Material Input – DMI) and consumption (Domestic Material Consumption – DMC) in the UK economy has declined since the start of the economic downturn in 2008. In 2012, DMI was 747.1 million tonnes (11.7 tonnes per capita) and DMC was 590.2 million tonnes (9.3 tonnes per capita).
Since 2000, the quantity of materials extracted for use1 in the UK has gradually declined and fell to 460.3 million metric tonnes in 2012, 7.7% lower than in 2011 (498.6 million tonnes). This represented 7.2 tonnes per capita (per person) in 2012.
Broadly, domestic extraction is divided into four categories:
biomass (material of biological origin that is not from fossil, including crops, wood and wild fish catch),
non-metallic minerals (consist mainly of construction and industrial minerals, including sand and gravel, limestone and gypsum, and clays),
fossil energy materials/carriers (including coal, peat, crude oil and natural gas), and
metal ores (including iron and non-ferrous metals).
Since 1990, the quantity of biomass extracted in the UK has remained fairly steady. In 2012, 164.5 million tonnes were extracted, 5.4% lower than in 2011 (173.9 million tonnes). Of this, crop residues, fodder crops and grazed biomass accounted for 73.1% (120.3 million tonnes).2
Figure 23 shows that the extraction of non-metallic minerals has considerably declined over the time series. In 2012, 195.6 million tonnes were extracted in comparison with 372.6 million tonnes in 1990. The majority of this fall is a result of falling demand for aggregates (granular material formed from natural rock substances). This is due to a combination of a decline in infrastructure projects, increased use of non-aggregate materials in buildings, less waste, and increased use of recycled aggregates in construction. The rapid decline observed from 2007 is related to the global economic downturn, which greatly reduced construction and demand for aggregates in the UK.
During the 1990s, extraction of fossil energy materials/carriers increased and peaked at 272.7 million tonnes in 1999. Since then, production has continually fallen and fell to 100.2 million tonnes in 2012, 13.1% lower than in 2011 (115.4 million tonnes). The decline in extraction of fossil energy materials is due primarily to a drop in North Sea oil and gas production, as major producing fields begin to decline and exploration of new fields is focused on smaller resources that are more difficult to exploit. The economic downturn has also had an effect.
Each year, a small quantity of metal ores is extracted in the UK, although this has notably decreased since 1990. The main metal extracted during the 1990’s was tin, but this is currently only produced in minor quantities. Iron was extracted until 2008, but is now no longer produced. In 2012, there were just 1,000 tonnes of metal ores extracted in the UK, a fall of 71.5% from 3,507 tonnes in 2011.
Figure 24 shows the total quantity of materials imported to and exported from the UK. While physical imports have largely increased over the period (rising from 210.2 million tonnes in 2000 to a peak of 295.0 million tonnes in 2007, before falling and then rising again), physical exports have gradually decreased (peaking at 196.7 million tonnes in 2002 and falling to 153.5 million tonnes in 2009). The rise in imports partly offsets the decline in domestic extraction.
In 2012, there were 4.5 tonnes of imports per capita and 2.5 tonnes of exports per capita.
Across the 2000 to 2012 period, fossil energy materials/carriers were the largest component of UK imports and exports. Trade in other materials fluctuated over the series, particularly in 2009 when there was a sharp drop in the trade of metal ores and concentrates. Compared with 2008, imports of metal ores and concentrates fell by 36.7% and exports fell by 23.8%. This is likely to be due to the economic downturn.
The Physical Trade Balance (PTB) shows the relationship between imports and exports and is calculated by subtracting the weight of exports from the weight of imports.3 The UK has a positive PTB, meaning that more materials and products are imported than are exported.
In 2000, the PTB was relatively small at 15.7 million tonnes. It generally increased until 2007, but then fell in 2008, 2009 and 2010 during the economic downturn. However, the PTB has since increased and peaked at 129.9 million tonnes in 2012. In 2012, the total mass of imports (286.8 million tonnes) was almost double the total mass of exports (157.0 million tonnes). The widening gap between physical imports and exports suggests that the UK is becoming more reliant on the production of materials in other countries.
Direct Material Input (DMI) (Domestic extraction + Imports) measures the total amount of materials that are available for use in the economy.
Domestic Material Consumption (DMC) (Domestic extraction + Imports – Exports) measures the amount of materials used in the economy, and is calculated by subtracting exports from DMI.
Figure 25 shows that DMI and DMC were fairly stable between 2000 and 2007 but then gradually declined from 2008 at the start of the economic downturn, showing that fewer materials were being used and consumed in the UK economy. DMI and DMC fell most sharply in 2009, by 10.5% and 10.9% respectively. Since then, they have been steadier, although they fell slightly in 2012 to 747.1 million tonnes for DMI and 590.2 million tonnes for DMC, the lowest levels recorded across the series.
Within DMC, non-metallic minerals was the largest component over the 2000 to 2012 period, although their use fell sharply in 2009 and have since remained at a similar level to the consumption of biomass and fossil fuels. In 2012, non-metallic minerals and biomass each accounted for 33.0% and fossil fuels accounted for 31.0% of DMC. The remaining 2.9% consisted of metal ores and other products.
In 2012, DMI represented 11.7 tonnes per capita and DMC represented 9.3 tonnes per capita.
For more data on material flows and indicators, see the Material flows account (175.5 Kb Excel sheet) dataset.
At present, DMC is the most prominent material flows indicator used across Europe.
In 2011, aggregated DMC for the EU-27 member states equalled 7.4 billion tonnes, which represented 14.7 tonnes per capita. Germany had the highest DMC at 1.4 billion tonnes, followed by France and Poland at 0.8 billion tonnes, and Italy and the UK at 0.6 billion tonnes.
Figure 26 shows DMC per capita for each EU-28 member state in 2011. Finland had the highest DMC per capita at 35.1 tonnes, followed by Ireland (26.9 tonnes), Estonia (26.8 tonnes), Austria (22.4 tonnes) and Sweden (22.3 tonnes). Seventeen member states fell in the range of +/-5 tonnes of the EU-27 average. Densely populated countries, including the UK (9.7 tonnes per capita), often consume lower amounts of materials per person than the EU average.
As well as variations in consumption rates, differences in quantities and composition of DMC between member states can also be explained according to different living standards and economic structures and development.
A limitation of the DMC indicator is its ‘asymmetry’: it measures the domestic extraction of material resources in tonnes of gross harvest and ore, whereas the imports are measured according to the weight of goods crossing the boundary independent of how far the imported products have been processed (Eurostat, 2012).4
The Raw Material Consumption (RMC) indicator is designed to overcome this asymmetry. In addition to domestic extraction, RMC includes imports expressed or converted into their Raw Material Equivalents (RME) (into equivalents of domestic extraction from the rest of the world to produce the respective goods).
Figure 27 shows the RMC indicator compared with the DMC indicator. Both exclude fossil energy materials/carriers.
RMC estimates peaked in 2001 at 616.9 million tonnes, which was 16.6% higher than DMC at 529.1 million tonnes.
In 2012, RMC was 485.0 million tonnes, which was 19.1% greater than DMC at 407.1 million tonnes. RMC consisted of:
207.9 million tonnes of biomass,
54.6 million tonnes of metal ores, and
222.4 million tonnes of non-metallic minerals.
DMC consisted of:
194.8 million tonnes of biomass,
9.9 million tonnes of metal ores,
195.0 million tonnes of non-metallic minerals, and
7.4 million tonnes of other products.
Water use is the physical amount of water removed (abstracted) from any source for consumption and production activities. In 2011, total water abstraction from freshwater (non-tidal) sources in England and Wales was 10,463 million cubic metres. Of this, 58.1% was for public water supply, while 41.9% was directly abstracted by different sectors of the economy.
Public water supply is the use of mains water supplied by water companies to various sectors of the economy, including households, the manufacturing sector, and services.
Of all public water supply, 47.7% was used by households, while non-domestic sectors accounted for the remaining 52.3% of public water use. The services sector used 9.7%, the manufacturing sector used 4.3%, while 18.6% was lost through leakage. Significant non-domestic users of the public water supply were the chemicals and chemical products sector (165.9 million cubic metres), and accommodation and food services sector (127.0 million cubic metres).
In 2011, direct abstraction accounted for 41.9% of freshwater (non-tidal) abstraction in England and Wales.
The sector that directly abstracted the largest amount of water was electricity generation, directly abstracting 2,537.6 million cubic metres (57.9% of total direct abstraction). The agriculture, forestry and fishing sector was also a major user, with 878.7 million cubic metres directly abstracted (20.1% of total direct abstraction) in addition to the 120.5 million cubic metres taken from the public water supply. The manufacturing sector directly abstracted 11.0% of total direct abstraction, while also using 4.3% of the public water supply.
An environmental tax is a tax on a physical unit (for example, petrol or a passenger flight) that has a proven negative impact on the environment. Such taxes are important policy instruments for pollution control and natural resource management. Their main aim is to influence economic behaviour and reduce damaging effects on the environment.
Revenue from environmentally related taxes (in current prices) has gradually increased over the past two decades, peaking at £43.0 billion in 2013. This represented 7.5% of total revenue from taxes and social contributions in the UK and was equivalent to 2.7% of Gross Domestic Product (GDP).
In 2013, total revenue from energy taxes was £31.1 billion, which represented 72.4% of total environmental taxes. The largest contributor to energy taxes was taxes on hydrocarbon oils (fuels) at £26.7 billion.
Environmental taxes can be divided into three types: energy, transport, and pollution/resources.
Figure 30 shows that the amount of revenue received by the UK government from environmentally related taxes has gradually increased since the series began in 1993, peaking at £43.0 billion in 2013. This was 4.0% higher than in 2012, when revenue was £41.3 billion. This growth was driven by increases of 2.7 percentage points from energy taxes, 1.0 percentage point from transport taxes, and 0.3 percentage points from pollution/resource taxes.
The main exception to this trend occurred in 2001, where total environmental tax revenue decreased by 3.1% compared with the previous year. This was driven by a £1.0 billion decrease in taxes on hydrocarbon oils (fuels) and a £0.6 billion decrease in motor vehicle duties paid by businesses. This followed a series of national fuel protests in the autumn of 2000 and a change in the basis for vehicle tax (see Transport taxes below).
In 2013, revenue from environmentally related taxes was equivalent to 2.7% of Gross Domestic Product (GDP). In addition, they accounted for 7.5% of revenue from total taxes and social contributions in the UK.
Energy taxes consist of taxes on energy production and on energy products used for both transport and stationary purposes. They include:
taxes on hydrocarbon oils (fuels),
climate change levy,
fossil fuel levy,
renewable energy obligations,
emissions trading scheme (EU-ETS), and
carbon reduction commitments,
although these were all introduced and collected at different times throughout the time series.1
In 2013, total revenue from energy taxes was £31.1 billion, an increase of 3.7% from £30.0 billion in 2012. This represented 72.4% of total environmental taxes. The increase in 2013 was due to large rises in revenue from the climate change levy (71.6%) and renewable energy obligations (29.6%).
The largest contributor to energy taxes is tax on hydrocarbon oils (including petrol and diesel). Over the past two decades, revenue from this tax has more than doubled, rising from £12.5 billion in 1993 to £26.7 billion in 2013. In 2013, this tax accounted for 85.8% of total energy tax revenue.
In 2013, revenue from energy taxes was equivalent to 1.9% of GDP.
Transport taxes consist mainly of taxes related to the ownership and use of motor vehicles, although taxes on other transport and related transport services are also included.
Total revenue from transport taxes in 2013 was £10.3 billion, which represented a 4.2% increase from £9.9 billion in 2012. This was largely due to a 7.0% increase in revenue from air passenger duty. In 2013, transport taxes revenue accounted for 24.1% of total environmental taxes.
Revenue from transport taxes has generally increased over the 1993 to 2013 period, although there have been a few fluctuations. For example, in terms of decreases, there was a large fall in revenue from motor vehicle taxes paid by businesses in 2001. This may be due to the change from vehicle tax being based on engine size (for cars and light goods vehicles registered before 1 March 2001) to being based on fuel type and CO2 emissions (for cars and light goods vehicles registered on or after 1 March 2001). In terms of increases, for example, the rate of air passenger duty doubled in 2007, which contributed 5.9 percentage points to the 23.5% rise in transport tax revenue for that year.
The highest contributor to transport taxes is tax on motor vehicles from households. Since the start of the series, revenue from this tax has increased more than two-fold from £2.3 billion in 1993 to £5.1 billion in 2013. This tax accounted for 49.5% of total transport taxes revenue in 2013.
In 2013, revenue from transport taxes was equivalent to 0.6% of GDP.
Pollution and resource taxes are related to the management of solid waste and activities linked to the extraction and use of natural resources. In the UK, they include landfill tax, aggregates levy (a tax on the commercial exploitation of rock, sand and gravel) and fishing licences.
Pollution and resource tax revenue contributes the smallest proportion to the total of environmental taxes. In 2013, revenue was £1.5 billion, a 10.3% increase from £1.4 billion in 2012. This increase was largely due to the increase in landfill tax revenue.
The largest contributor to pollution and resource tax revenue is landfill tax. Revenue has generally increased since its introduction in 1996 and peaked at £1.2 billion in 2013, which represented 80.3% of total pollution and resource taxes.
In 2013, revenue from pollution and resource taxes was equivalent to 0.1% of GDP.
For more data on environmental taxes, see the Environmental taxes (59.5 Kb Excel sheet) dataset.
In 2012, the EU-28 raised a total of €311.7 billion from environmental taxes.2 This was equivalent to 2.4% of Europe’s GDP and represented 6.0% of total revenues from taxes and social contributions.
Germany had the highest revenue at €58.0 billion. This was followed by the UK (€50.7 billion), Italy (€47.3 billion), France (€37.2 billion) and the Netherlands (€21.3 billion).
Of the total environmental tax revenue for the EU-28 in 2012, energy taxes represented 75.0%, transport taxes represented 20.7% and pollution/resource taxes represented 4.3%.
Figure 31 shows the environmentally related tax revenue as an equivalent percentage of national GDP for the EU-28 member states in 2012. Denmark collected the highest proportion of taxes (3.9%), followed by Slovenia (3.8%), the Netherlands (3.6%), Croatia (3.2%) and Finland (3.1%). Spain (1.6%), Lithuania (1.7%), Slovakia (1.8%), France (1.8%) and Romania (1.9%) were the only countries where environmental taxes as a GDP equivalent were less than 2.0%.
Environmental taxes data produced by ONS are based on the definition outlined in Regulation (EU) No 691/2011 on European environmental economic accounts. To comply with this Regulation, ONS submits UK data to Eurostat (the European statistical office) annually.
In 2010, the UK’s coalition government committed to increasing the proportion of revenue from environmental taxes.3 To measure this, HM Treasury have developed a separate definition based on the following principles:
the tax is explicitly linked to the government’s environmental objectives,
the primary objective of the tax is to encourage environmentally positive behaviour change, and
the tax is structured in relation to environmental objectives, for example: the more polluting the behaviour, the greater the tax levied.
This definition includes the following six taxes: climate change levy, aggregates levy, landfill tax, EU emissions trading scheme (EU-ETS), carbon reduction commitment, and carbon price floor. This is narrower than the definition used by ONS (Table 3), meaning that total environmental taxes data published by HM Treasury are much lower than the figures included in this release. For example, HM Treasury’s latest figures show that environmental tax revenue in 2011/12 was £3.1 billion. In contrast, ONS figures show that revenue from environmentally related taxes was £40.2 billion in 2011 and £41.3 billion in 2012.
|ONS definition||HM Treasury definition|
|Tax on Hydrocarbon oils||Carbon Price Floor1|
|Climate Change Levy1||Climate Change Levy|
|Fossil Fuel Levy|
|Renewable Energy Obligations|
|Emissions Trading Scheme (EU-ETS)||Emissions Trading Scheme (EU-ETS)|
|Carbon Reduction Commitment||Carbon Reduction Commitments|
|Air Passenger Duty|
|Rail Franchise Premia|
|Northern Ireland Driver Vehicle Agency|
|Motor Vehicle Duties Paid by Businesses|
|Motor Vehicle Duty Paid by Households|
|Land Fill Tax||Landfill tax|
|Aggregates levy||Aggregates Levy|
Environmental taxes data are currently available for 1993 to 2013. Some taxes were introduced and collected at different times throughout the time series. In terms of energy taxes:
Taxes on hydrocarbon oils (fuels) – these have been collected throughout the whole time series. Rates are decided by the Chancellor on a budget-by-budget basis, taking relevant economic, social and environmental factors into account.
Climate change levy - this is a tax on non-domestic use of energy and was introduced in April 2001 under the Finance Act 2000, forming part of the UK’s Climate Change Programme. Data are included for 2001 onwards. From 1 April 2013, it also includes Carbon Price Floor taxes.
Fossil fuel levy – this was effectively replaced by the climate change levy. Fossil fuel levy rates, controlled by OFGEM, have been set to zero since April 2002 in England and Wales and November 2002 in Scotland. Data are therefore included up to 2002.
Gas levy – this was introduced following the Gas Levy Act 1981 but was later repealed by the Finance Act 1998. Data are therefore included up to 1998.
Hydro-Benefit – this was introduced in 1991 to protect energy consumers in remote areas from excessive charges resulting from the increased costs of supplying those areas. However, it was abolished in 2004 because it contravened European law, although Scottish and Southern Energy continued the scheme on a voluntary basis until April 2005. Data are therefore included for 1993 to 2005.
Renewable Energy Obligations – this was introduced in 2002 to provide incentives for the deployment of large scale renewable electricity in the UK. Data are therefore included for 2002 onwards.
Emissions Trading Scheme (EU-ETS) – this is the largest multi-country, multi-sector greenhouse gas emissions trading scheme in the world and it is central to the EU meeting its emissions reduction target of 20% by 2020. Data are included for 2009 onwards.
Carbon Reduction Commitment – this energy efficiency scheme is designed to improve energy efficiency and cut emissions in large public and private sector organisations. It targets emissions not already covered by Climate Change Agreements and the EU-ETS. Data are included for 2012 onwards.
Environmental protection expenditure (EPE) includes all activities and actions which have as their main purpose the prevention, reduction, and elimination of pollution or any other degradation of the environment. The purpose of reporting EPE is to enable identification and measurement of society’s response to environmental concerns through the supply of and demand for environmental protection services and through the adoption of production and consumption behaviour aimed at preventing environmental degradation.
In 2012, the UK government spent £14.2 billion on environmental protection activities, of which £11.5 billion (81.3%) was spent on the collection, treatment and disposal of waste.
Government expenditure on environmental protection as an equivalent of Gross Domestic Product (GDP) has steadily increased since 1996 and despite the economic downturn it has remained equivalent to between 0.9 and 1.0% of GDP since 2006.
The extraction, manufacturing, and electricity, gas and water industries spent £3.2 billion on environmental protection in 2012, the greatest proportions of which were spent on waste water management (£956.5 million, 30.3%) and waste management (£853.5 million, 27.0%).
EPE is currently reported for two sectors: EPE by general government and EPE by industry.1
EPE by general government figures are derived using annual expenditure data broken down by function using the Classification Of Functions Of Government (COFOG)2, sourced from the UK National Accounts. At present, there are two methods for estimating EPE by general government in the UK.3 The main difference relates to expenditure on investments.4
Figure 32 shows EPE by general government for 1996 to 2012. Both series (EPE including investments and EPE excluding investments) show that there has been a general increase in expenditure since 1996, apart from falls in 2005 (including investments), 2008, 2011 and 2012.
The most notable difference in EPE between the two series was observed in 2005 and is due to the decommissioning of British Nuclear Fuels plc (BNFL). In April 2005, BNFL (classified as a public corporation) transferred some nuclear reactors to the Nuclear Decommissioning Authority (NDA) (classified as central government). The value of the transfer was -£15.6 billion. The negative value reflects the fact that the reactors were at the end of their productive lives and had large decommissioning and clean-up liabilities. This transfer did not affect overall economic figures as it was an acquisition by one sector and a disposal by another. However, it particularly affects the investments element of the EPE series. Excluding investments, EPE by general government was £22.5 billion in 2005. But when investments are taken into account (-£14.4 billion), EPE was reduced to £8.1 billion.
The preferred method in European environmental accounting for reporting EPE is to include investment expenditure and this series will be the focus of the remainder of this section.
In 2012, general government spent £14.2 billion on environmental protection, £0.1 billion less than in 2011 (£14.3 billion). This was equivalent to 0.9% of Gross Domestic Product (GDP).
EPE by general government peaked in 2010 at £15.1 billion, which was largely due to an increase in investment grants towards pollution abatement in that year.
Figure 33 shows that EPE by general government as an equivalent of GDP has generally increased since 1996 (0.4%) (apart from in 2005 for the reason outlined above and in 2008) and despite the economic downturn, it has remained between 0.9% and 1.0% since 2006.
Figure 34 shows the main environmental protection activities funded by general government.
The largest amount of EPE is spent on waste management. This includes the collection, treatment and disposal of waste. There was a sharp increase in waste management expenditure in 2006, which reflects ongoing costs following the decommissioning of BNFL in 2005. In 2012, spending on waste management amounted to £11.5 billion, £0.1 billion more than in 2011 (£11.4 billion).
In 2012, a further £0.8 billion was spent on the protection of biodiversity and landscape (£0.4 billion) and research and development (£0.4 billion), and £0.2 billion was spent on pollution abatement. Of the remainder2, general government spent £1.7 billion.
Figure 35 shows EPE by general government for each of the EU-28 member states in 2012.
In 2012, governments in the EU-28 spent a total of €106.5 billion on environmental protection activities. This was equivalent to 0.8% of Europe’s GDP.
France spent the most on environmental protection at €22.3 billion, followed by the UK at €17.5 billion, Germany at €15.6 billion, Italy at €14.0 billion and the Netherlands at €10.0 billion.
As an equivalent of national GDP, Figure 35 shows that general government EPE was highest in the Netherlands at 1.7%, followed by Malta (1.5%), Czech Republic (1.4%), Luxembourg (1.3%) and France (1.1%). These were closely followed by the UK (0.9%).
EPE by industry figures are estimated using the results of an annual survey commissioned by the Department for Environment, Food and Rural Affairs (Defra).5
In total, it is estimated that UK industries spent £3.2 billion on environmental protection activities in 2012. The electricity, gas and water supply industries spent the most at £759.6 million, followed by the food, beverages & tobacco products industries at £388.8 million.
Figure 36 shows total EPE by industry according to activity. In 2012, the greatest amount was directed towards waste water management at £956.5 million (30.3%). This was followed by expenditure on waste management at £853.5 million (27.0%).
Figure 37 shows total EPE by industry in 2012, split by operating expenditure (Opex) (in-house operating costs of a company’s own environmental protection activities), capital expenditure (Capex) (integrated and ‘end of pipe’ investments, for example the purchase of equipment to reduce or eliminate emissions as part of the production processes, or to clean up at the end), and expenditure on research and development.
Across most industries, Opex accounted for the greatest proportion of their EPE. The proportion of Opex was highest in the 'Basic and fabricated metals' industry at 92.6%, but lowest in the 'Other machinery and equipment' industries at 42.9%. Notably, the 'Other machinery and equipment' industries spent a similar proportion on research and development activities at 44.7%. The proportion of Capex was greatest within the 'Coke and refined petroleum' industry at 30.3%, although their total EPE was smallest at £37.3 million.
More data on EPE by general government are available in the Environmental protection expenditure: by general government (51.5 Kb Excel sheet) dataset.
More data and information on EPE by industry are available in the
Environmental protection expenditure: by industry (90 Kb Excel sheet)
dataset and on the Department for Environment, Food and Rural Affairs website.
Since the publication of UK Environmental Accounts 2013, there have been revisions and updates to some of the accounts. These are largely due to revisions in data sources and improvements to methodology.
Revisions to atmospheric emissions and energy data are primarily due to:
revisions to the core energy statistics presented in the Digest of UK Energy Statistics (DUKES),
revisions to the inventory methodologies and emission factors based on new evidence,
revisions to other datasets or to the additional details used to generate the detailed industry splits from the core UK inventory categories (for example, sharing road transport among the industry sectors), and
the adoption of methodologies to reflect inclusion of newly compiled sources.
Updates, particularly those involving revised methodologies, may affect the whole time series, so estimates of emissions for a given year may differ from estimates of emissions for the same year reported previously.
Table 4 shows the differences in air emissions and energy consumption estimates published in UK Environmental Accounts, 2013 and 2014.
|Greenhouse gas emissions1 2013||806,495||754,413||734,055||739,458||671,152||634,765|
|Acid rain precursor emissions2 2013||6,910||5,090||3,542||3,156||2,164||2,101|
|Energy consumption3 2013||222||226||241||248||226||213|
|Greenhouse gas emissions1 2014||814,549||768,913||750,356||755,884||680,160||642,038|
|Acid rain precursor emissions2 2014||6,900||5,087||3,551||3,175||2,114||2,053|
|Energy consumption3 2014||222||227||241||248||225||212|
|Greenhouse gas emissions % change||1.0||1.9||2.2||2.2||1.3||1.1|
|Acid rain precursor emissions % change||-0.1||-0.1||0.2||0.6||-2.3||-2.3|
|Energy consumption % change||0.1||0.1||0.1||0.0||-0.3||-0.4|
Greenhouse gas emissions have been revised upwards. This is due to the inclusion of new sources (mainly autogenerators use of biogas from anaerobic digestion), and revisions and restructuring of existing sources (particularly agricultural livestock and landfill). However, at the same time, cross boundary sources (those used to make adjustments for the ‘residence’ principle) were revised downwards.
Acid rain precursor emissions have been revised downwards for 1990 to 1995, upwards for 1996 to 2007, and downwards for 2008 to 2011. The largest revisions were the downward revisions for the most recent years (-2.8% in 2008, -2.6% in 2009, and -2.3% in 2010 and 2011). This was mainly due to cross boundary revisions.
Energy consumption figures have remained fairly constant between 1990 and 2007, but were revised downwards in 2008 (-0.8%), 2009 (-0.2%), 2010 (-0.3%) and 2011 (-0.4%). These changes are due in most part to DUKES revisions in gas oil and fuel oil totals, which have been reduced by around 16-18%, as well as a smaller revision to natural gas use in 2008.
An Improvements to UK Environmental Accounts (101.1 Kb Pdf) paper (published in May 2014) details the revisions that have been applied to the material flow account. In summary, changes have been made to data sources and methodology to bring the account in line with European regulation requirements.
Table 5 shows the differences between estimates published in UK Environmental Accounts, 2013 and 2014.
|Million metric tonnes|
|Domestic extraction 2013||673||584||447||428|
|Direct Material Input (DMI) 2013||883||862||709||707|
|Domestic Material Consumption (DMC) 2013||686||687||544||545|
|Domestic extraction 2014||739||644||514||499|
|Direct Material Input (DMI) 2014||949||923||778||775|
|Domestic Material Consumption (DMC) 2014||755||746||612||612|
|Domestic extraction % change||9.7||10.2||15.1||16.4|
|Imports % change||0.8||0.9||0.7||-0.5|
|Exports % change||-1.1||1.3||0.5||0.8|
|Direct Material Input (DMI) % change||7.5||7.1||9.7||9.7|
|Domestic Material Consumption (DMC) % change||10.0||8.6||12.5||12.3|
On average, domestic extraction figures increased by 12% each year between 2000 and 2011. This was largely due to increases in biomass totals, which rose by an average of 65% each year. This was mainly a result of the addition of fodder crops and crop residues (considered to be ‘used’ extraction as they have further economic uses), produced using an estimation tool developed by Eurostat.
As a result of the increases to domestic extraction, the Direct Material Input (DMI) and Domestic Material Consumption (DMC) indicators also increased, by 8% and 10% respectively each year on average.
An improved method was used to allocate physical imports and exports to material categories in 2014, but this only had a small impact on the figures when compared with those published in 2013.
An Improvements to UK Environmental Accounts (101.1 Kb Pdf) paper (published in May 2014) details the revisions that have been applied to the environmental taxes account. In summary, changes have been made to the list of taxes included to bring the account in line with European regulation requirements.
Table 6 shows the differences between estimates published in UK Environmental Accounts, 2013 and 2014.
Total environmental taxes decreased between 8% and 12% each year between 1993 and 2011. This was primarily due to the exclusion of VAT on duty in 2014 figures.
As part of the ONS Natural Capital Roadmap (786.5 Kb Pdf) , ONS aims to incorporate natural capital fully in to the UK Environmental Accounts by 2020. In June 2013, ONS published experimental accounts and methodologies of UK land use (527.8 Kb Pdf) , woodland area (197.6 Kb Pdf) , non-monetary timber resources (197.6 Kb Pdf) , monetary timber resources (226.6 Kb Pdf) , and woodland ecosystem assets and services (273.5 Kb Pdf) . These accounts are included in this bulletin as experimental statistics. These are all prepared in accordance with the System of Environmental-Economic Accounting Central Framework (SEEA CF) and the System of Environmental-Economic Accounting Experimental Ecosystem Accounting (SEEA EEA).
These accounts are experimental and under development and therefore they should be interpreted in this context.
Land use can be defined as the activities undertaken, or the changes made to an area, for the purpose of economic production or for the maintenance and restoration of an environmental function (System of Environmental-Economic Accounting).
Table 7 (117 Kb Excel sheet) shows the non-monetary land use asset account for the UK for 2000 to 2010.
Figure 38 shows that agriculture1 comprised the largest area of land use in the UK, which spanned 15.3 million hectares in 2010. This was equivalent to 65.4% of the total land area of the UK. Relative to its size, the area of land used for agriculture changed the least during the 2000 to 2010 period, with an overall increase of just 0.2% (equivalent to 35 thousand hectares).
Within agriculture, the largest decrease in land use area proportional to its size was other farmland (for example, roads, buildings and yards). The total area of other farmland fell by 156 thousand hectares to 492 thousand hectares, a decrease of 24.1%.
Despite agriculture having the smallest relative change in area, it contains the two sub-categories with both the largest increase (permanent grassland) and decrease (rough grazing) in physical area. Permanent grassland had the largest physical increase in land use from 2000 to 2010, which increased by 505 thousand hectares (10.6%)2. The largest physical decrease in land use area during this period was rough grazing with a reduction of 297 thousand hectares (7.1%).
In 2010, forestry compromised 13.1% of total UK area, equivalent to 3.1 million hectares, and the second largest category of UK land use. Forestry can be split into broadleaved and coniferous woodland, which covered 1.4 million hectares (6.2% of total UK area) and 1.6 million hectares (6.8% of total UK area) respectively.
Freshwater comprised the smallest area of land used in the UK. Freshwater spanned 0.2 million hectares, which is equivalent to 1.1% of the total area of the UK. Relative to its size, freshwater increased the most from 2000 to 2010, with an increase of 17.5% (equivalent to 37 thousand hectares).
Agriculture includes land used for crops and bare fallow (including horticulture), rough grazing (sole right), permanent grassland, temporary grassland and other farmland including roads, buildings and yards.
This is a result of the change of data source, and thus grassland definitions, in 2004, from the Integrated Administration and Control System (IACS) to the Single Payment Scheme (SPS). SPS includes significantly more overall grassland than IACS and has differing definitions for the grassland types, particularly temporary and permanent grassland. See Changes in the Area of Grassland in England, Defra, May 2010.
This section includes 4 accounts:
Non-monetary timber asset account,
Monetary timber asset account, and
Non-monetary woodland ecosystem account.
The total woodland area in the UK was 3,138.4 thousand hectares in 2014. Of the total woodland area:
1,301.6 thousand hectares were located in England,
306.3 thousand hectares were located in Wales,
111.5 thousand hectares were located in Northern Ireland, and
1,419.0 thousand hectares were located in Scotland.
The steady growth in UK woodland over the past century is shown in Figure 39. Much of the increase between 1924 and 2014 can be explained by new conifer plantations created between the 1950s and 1980s, although some apparent changes will have occurred as a result in changes in the definitions and methodology used by each woodland survey.
Table 8 (143.5 Kb Excel sheet) shows the UK woodland area account for 2013–2014, which is based on the methodology published by ONS in June 2013. This methodology paper explores the limitations of this approach and the need for a balancing item in more detail.
Additions to stock relate to new planting, with the largest increase coming from new planting of broadleaves in other woodland. Reliable estimates of reductions in stock (or woodland loss) are not available. A balancing item has been included to record any differences between the opening and closing stocks resulting from changes in ownership and changes in assumptions about the conifer/ broadleaf breakdown of this woodland area.
The total stock of standing timber resources in the UK was estimated at 585.3 million cubic metres overbark in 20112. Of the total stock of standing timber resources in 2011:
268.5 million cubic metres overbark were located in England,
60.5 million cubic metres overbark were located in Wales,
246.4 million cubic metres overbark were located in Scotland, and
9.8 million cubic metres overbark were located in Northern Ireland.
Table 9 (143.5 Kb Excel sheet) shows the non-monetary asset account for UK timber resources for 2011-12, which is based on the methodology published by ONS in June 2013. This account is currently under development and some of the breakdowns are based on expert opinion.
Table 9 shows that the majority of removals (harvesting) was coniferous timber (also known as softwood) - a total of 11.0 million cubic metres overbark of coniferous timber was removed compared to broadleaf (or hardwood) removals of 0.6 million cubic metres overbark. The closing stock is based on a residual and estimates 594.6 million cubic metres overbark as at 31 March 2012, an increase of 1.6%. The other categories cannot be commented on reliably at this time due to data limitations.
The value of timber presented here is its value as standing timber before felling, extraction and processing, and represents the value accruing from the timber resource itself. Table 10 (143.5 Kb Excel sheet) shows the experimental monetary asset account for UK timber resources for 2011–12, which is based on the methodology published by ONS in June 2013. This account is currently under development and includes a number of underlying assumptions:
The stumpage price is the same across all timber resources.
The stumpage price is received when the timber is harvested. The harvesting age is 50 years and discounted appropriately with HM Treasury (2003) discount rates.
All timber is available for wood supply.
As the timber grows until it is harvested, the expected volume of standing timber for each age class is fixed at harvesting age.
Table 10 (143.5 Kb Excel sheet) shows that the experimental monetary value of UK timber resources at 31 March 2012 is estimated to be around £6.8 billion.
The tables presented in the methodology paper published in June 2013 are reproduced here ( Tables 11 and 12 (143.5 Kb Excel sheet) ), and it is anticipated that once these have been further developed to a more robust standard, accompanying commentary can then be formed. This ecosystem account consists of two sub-accounts, an ecosystem asset account and an ecosystem service account.
Ecosystem assets are environmental assets, for example, a woodland area. An ecosystem asset account provides an accounting framework for these assets, split into two broad areas; the extent of the ecosystem asset, for example, how many hectares of woodland exist, and the condition of the ecosystem asset, for example, a measure of tree health.
Ecosystem services are central in the ecosystem accounting framework since they provide the link between ecosystem assets on the one hand and the benefits received by society on the other. People benefit from both the materials that ecosystems provide (such as the harvesting of timber from woodland) and from the outcomes of natural processes (such as the benefits from clean air that has been filtered by an ecosystem).
Ecosystem services that contribute to human well-being are classified into:
Provisioning services – these are generally the material products that ecosystems provide, for example, food (crops, meat and dairy products, fish and honey), or water.
Regulating services – these are the benefits provided by ecosystems in the regulation of various aspects of the planet, for example, climate regulation; noise and air pollution reduction, and flood hazard reduction.
Cultural services – non-material benefits, for example, through cultural heritage; recreation or aesthetic experience.
Supporting services – such as biodiversity, soil function – these are not accounted for separately in order to avoid double-counting.
FC/NRW/FS represent the public woodland bodies of Forestry Commission, Natural Resources Wales and Forest Service. Other represents private woodland owners and other public woodland owners (such as Local Authorities). It should be noted that the Forestry Commission’s functions in Wales transferred to a new organisation on 1 April 2013, combining with the Environment Agency in Wales and Countryside Council for Wales to form Natural Resources Wales (NRW). The figures presented here only relate to areas that were previously owned/managed by Forestry Commission Wales, not any woodland areas that were previously owned/managed by the Environment Agency in Wales or Countryside Council for Wales.
Overbark is the volume of timber including the bark.
Context and use of the statistics
In the early 1990’s, government research on resource accounting recommended satellite accounting and the Office for National Statistics (ONS) published an article on environmental issues and the National Accounts. ONS then established a small unit supported by an expert advisory panel and published pilot UK environmental accounts. In 1999, ONS published the first regular UK environmental accounts alongside National Accounts in the annual Blue Book. Since then, the accounts have continually developed in line with international best practice.
Regulation (EU) No 691/2011 on European environmental economic accounts requires Member States to produce data on air emissions, environmental taxes, and economy-wide material flow accounts annually. These were required on an obligatory basis for the first time in 2013 (before this, the UK submitted data on a voluntary basis). European environmental accounts data can be found in Eurostat’s environmental accounts databases.
Regulation (EU) No 538/2014 (amending Regulation (EU) No 691/2011) on European environmental economic accounts adds a further three modules on environmental protection expenditure, the environmental goods and services sector, and physical energy flow accounts. These are currently under development and are required on an obligatory basis in 2017.
Environmental accounts are used nationally and internationally, primarily by governments, development organisations and researchers, to inform sustainable development policy, to evaluate the environmental impacts of different sectors of the economy, and to model impacts of fiscal or monetary measures.
Further information is available in the
Uses of UK Environmental Accounts (19.6 Kb Pdf)
Environmental Good and Services Sector
To comply with Regulation (EU) No 538/2014 by 2017, work is currently ongoing at ONS to produce estimates on the Environmental Goods and Services Sector (EGSS). The estimates will contain data on turnover, value added, employment and exports of the environmental goods and services sector. These will be published UK Environmental Accounts, 2015.
Quality and methodology
The industry classification used in UK Environmental Accounts, 2014 is the Standard Industrial Classification 2007.
Measuring National Well-being
The UK Environmental Accounts are an output of the Measuring National Well-being Programme. The programme aims to produce accepted and trusted measures of the well-being of the nation and how the UK as a whole is doing.
Find out more on the Measuring National Well-being pages on the ONS website.
Details of the policy governing the release of new data are available by visiting www.statisticsauthority.gov.uk/assessment/code-of-practice/index.html or from the Media Relations Office email: email@example.com
The United Kingdom Statistics Authority has designated these statistics as National Statistics, in accordance with the Statistics and Registration Service Act 2007 and signifying compliance with the Code of Practice for Official Statistics.
Designation can be broadly interpreted to mean that the statistics:
Once statistics have been designated as National Statistics it is a statutory requirement that the Code of Practice shall continue to be observed.
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