Soil nutrient balances England, 2020 - statistics notice
Updated 1 March 2024
Soil nutrient balances provide a method for estimating the annual nutrient loadings of nitrogen and phosphorus to agricultural soils. They give an indication of the potential risk associated with losses of nutrients to the environment; losses which can impact on air and water quality and on climate change. The nutrient balances are used as a high-level indicator of farming’s pressure on the environment and of how that pressure is changing over time. The balances do not estimate the actual losses of nutrients to the environment, but significant nutrient surpluses are directly linked with losses to the environment.
Nutrient balances are of direct relevance to policies relating to agriculture and the environment including climate change, air quality, water quality and habitats and biodiversity.
Key messages
Nitrogen
Provisional estimates for 2020 show the nitrogen balance:
- to be a surplus of 88 kg/ha of managed agricultural land
- increased 10 kg/ha (13%) compared to 2019
- decreased 20 kg/ha (18%) compared to 2000
Phosphorous
Provisional estimates for 2020 show the phosphorus balance:
- to be a surplus of 6.1 kg/ha of managed agricultural land
- increased 2.8 kg/ha (86%) compared to 2019
- decreased 3.0 kg/ha (33%) compared to 2000
1. England Nitrogen Balance
Figure 1. Summary of Nitrogen balance for England, 2000 to 2020 (kg N per hectare)
For the period 2019 to 2020 the key points are:
- The surplus of 88.1 kg/ha in 2020 is a decrease of 10.1 kg/ha (13%) compared to 2019. This has been driven by a 19.2 kg/ha (17%) decrease in offtake (mainly via harvested crops) while inputs (mainly from inorganic manufactured fertilisers and livestock manures) decreased by 9.1 kg/ha (4.7%) over the same period.
- The 2020 crop year saw very challenging weather conditions for sowing, crop establishment and harvest. As a result cereal production fell significantly, especially compared to the high levels of production seen in 2019. This drove a large overall decline in offtake, which more than offset a fall in total inputs.
- The fall in inorganic fertilisers was due to a combination of a reduction in planted areas, a swing to spring cropping (particularly spring barley) and generally poor growing conditions throughout the crop year. Further details can be found in the 2020 British Survey of Fertiliser Practice report.
For the period 2000 to 2020 the key points are:
- A 20.0 kg/ha (18%) fall in the total surplus per hectare from 108.1 kg/ha to 88.1 kg/ha.
- The main driver has been a 50.5 kg/ha decrease in inputs (from 233.0 kg/ha to 182.5 kg/ha) due to decreases in the application of inorganic (manufactured) fertilisers and manure production (the result of lower livestock numbers). This has been partially offset by a reduction of 30.5 kg/ha in offtake (particularly forage) from 124.9 kg/ha to 94.3 kg/ha.
The series break in 2009 is due to changes in farm survey data collection.
Table 1.1. Nitrogen balance for England, 2000, 2019 and 2020 (kg N per hectare)
2000 | 2019 | prov. 2020 | Change 2019-2020 | Change 2000-2020 | |
---|---|---|---|---|---|
Total Inputs | 233.0 | 191.5 | 182.5 | -9.1 | -50.5 |
Total Outputs | 124.9 | 113.6 | 94.3 | -19.2 | -30.5 |
BALANCE (Inputs minus outputs) | 108.1 | 78.0 | 88.1 | -10.1 | -20.0 |
Table 1.2. Detailed nitrogen balance sheet results, 2000, 2019 and 2020 (thousand tonnes of N)
2000 | 2019 | prov. 2020 | Change 2019-2020 | Change 2000-2020 | |
---|---|---|---|---|---|
TOTAL INPUTS | 1,862 | 1,574 | 1,476 | -98 | -297 |
Fertilisers | 938 | 792 | 729 | -63 | -151 |
Inorganic fertilisers | 910 | 746 | 682 | -63 | -170 |
Total organic fertilisers | 28 | 47 | 47 | 0 | +18 |
Manures | 680 | 567 | 552 | -15 | -106 |
Livestock Manure Production | 697 | 581 | 566 | -15 | -109 |
Cattle | 439 | 358 | 351 | -8 | -75 |
Pigs | 62 | 45 | 44 | -1 | -18 |
Sheep and goats | 101 | 83 | 80 | -3 | -17 |
Poultry | 91 | 91 | 88 | -3 | +1 |
Other livestock | 6 | 4 | 4 | 0 | -1 |
Withdrawals | -17 | -14 | -14 | 0 | +3 |
Other inputs | 244 | 215 | 195 | -20 | -39 |
Atmospheric Deposition | 126 | 102 | 69 | -33 | -38 |
Biological fixation | 109 | 104 | 119 | +14 | -1 |
Seeds and Planting Material | 9 | 9 | 8 | -1 | -1 |
TOTAL OFFTAKE | 998 | 933 | 763 | -170 | -126 |
Total Harvested Crops | 496 | 532 | 381 | -151 | -26 |
Cereals | 398 | 421 | 281 | -140 | -38 |
Oil crops | 32 | 50 | 29 | -21 | +27 |
Pulses and Beans | 29 | 33 | 38 | +4 | -8 |
Industrial Crops | 15 | 10 | 15 | +5 | -2 |
Other Crops | 22 | 18 | 18 | 0 | -4 |
Total Forage | 491 | 390 | 374 | -16 | -100 |
Harvested Fodder Crops | 17 | 37 | 40 | +3 | +17 |
Pasture | 474 | 353 | 334 | -18 | -118 |
Crop residues | 11 | 12 | 9 | -3 | 0 |
BALANCE (Inputs minus Offtake) | 864 | 641 | 713 | +72 | -171 |
Managed area (thousand ha) excluding rough grazing | 7,994 | 8,219 | 8,091 | -127 | +186 |
2. England Phosphorus Balance
Figure 2. Summary of Phosphorus balance for England, 2000 to 2020 (kg P per hectare)
For the period 2019 to 2020 the key points are:
- The surplus of 6.1 kg/ha represents an increase of 2.8 kg/ha (86%) compared to 2019. This has been driven by a decrease of 3.1 kg/ha (16%) in offtake while inputs decreased by 0.3 kg/ha (1.5%) when compared to 2019. As with nitrogen, decreased production in harvested cereal crops significantly impacted the phosphate balance.
For the period 2000 to 2020 the key points are:
- A 3.0 kg/ha fall in the total surplus per hectare from 9.1 kg/ha in 2000 to 6.1 kg/ha in 2020 (33%).
- The main driver has been a reduction in inputs (from 30.0 to 22.1 kg/ha) reflecting reduced fertiliser application rates and manure production (due to declining livestock populations). Total offtake has decreased from 20.9 kg/ha to 16.0 kg/ha, largely due to reduced forage production.
- After remaining at a similar level from 2002 to 2007 there was a sharp fall in the surplus between 2007 and 2009. This was a result of increased offtake from harvested crops in 2008 and a sharp reduction in fertiliser applications in 2009. The surplus has since returned to levels more consistent with the longer term trend.
The series break in 2009 is due to changes in farm survey data collection.
Table 2.1. Phosphorus balance for England, 2000, 2019 and 2020 (kg P per hectare)
2000 | 2019 | prov. 2020 | Change 2019-2020 | Change 2000-2020 | |
---|---|---|---|---|---|
Total Inputs | 30.0 | 22.5 | 22.1 | -0.3 | -7.9 |
Total Offtake | 20.9 | 19.2 | 16.0 | -3.1 | -4.9 |
BALANCE (Inputs minus Offtake) | 9.1 | 3.3 | 6.1 | +2.8 | -3.0 |
Table 2.2. Detailed phosphorus balance sheet results, 2000, 2019 and 2020 (thousand tonnes of P)
2000 | 2019 | prov. 2020 | Change 2019-2020 | Change 2000-2020 | |
---|---|---|---|---|---|
TOTAL INPUTS | 240 | 185 | 179 | -6 | -61 |
Fertilisers | 115 | 79 | 76 | -3 | -38 |
Inorganic fertilisers | 97 | 53 | 51 | -3 | -46 |
Total organic fertilisers | 18 | 26 | 26 | 0 | +8 |
Manures | 121 | 101 | 98 | -3 | -23 |
Livestock Manure Production | 121 | 101 | 98 | -3 | -23 |
Cattle | 69 | 56 | 55 | -1 | -14 |
Pigs | 12 | 9 | 9 | 0 | -4 |
Sheep and goats | 16 | 13 | 12 | 0 | -3 |
Poultry | 22 | 22 | 21 | -1 | -1 |
Other livestock | 2 | 1 | 1 | 0 | -1 |
Withdrawals | 0 | 0 | 0 | 0 | 0 |
Other inputs | 5 | 5 | 4 | 0 | 0 |
Atmospheric Deposition | 3 | 3 | 3 | 0 | 0 |
Seeds and Planting Material | 2 | 2 | 1 | 0 | 0 |
TOTAL OFFTAKE | 167 | 158 | 130 | -28 | -38 |
Total Harvested Crops | 87 | 93 | 69 | -25 | -18 |
Cereals | 70 | 74 | 52 | -22 | -18 |
Oil crops | 7 | 10 | 6 | -4 | -1 |
Pulses and Beans | 3 | 4 | 4 | 0 | 1 |
Industrial Crops | 3 | 2 | 3 | +1 | 0 |
Other Crops | 3 | 3 | 3 | 0 | 0 |
Total Forage | 79 | 62 | 60 | -3 | -19 |
Harvested Fodder Crops | 3 | 7 | 7 | 0 | +4 |
Pasture | 76 | 55 | 52 | -3 | -23 |
Crop residues | 2 | 2 | 2 | 0 | 0 |
BALANCE (Inputs minus Offtake) | 73 | 27 | 49 | +22 | -24 |
Managed area (thousand ha) excluding rough grazing | 7,994 | 8,219 | 8,091 | -127 | +98 |
3. What you need to know about this release
This section ensures any important information is clearly explained so users do not misunderstand the data.
3.1. Contact details
Responsible statistician: James Maguire
Email address: agri.environmentstatistics@defra.gov.uk
Enquiries: 020 802 65783
Media enquiries: 0345 051 8486
Department for Environment, Food and Rural Affairs
2 Marsham Street
Westminster
London
SW1P 4JA
3.2. National and Official Statistics
Publications with National Statistics status meet the highest standards of trustworthiness, quality and public value, and it is our responsibility to maintain compliance with these standards.
These estimates are based on a methodology developed by the OECD and adopted by Eurostat (see the Methodology section at the end for more detail). Whilst this methodology is sound and allows meaningful comparisons between countries and over time, the specific data sources used within different countries will vary depending on the data available. The majority of the data sources used to calculate these nutrient balance estimates are designated as National Statistics. However, some of the data are from sources that do not have this designation and may have greater levels of uncertainty. As a result these estimates have been designated as Official Statistics.
For general enquiries about National and Official Statistics, contact the National Statistics Public Enquiry Service:
Tel: 0845 601 3034
Email: info@statistics.gov.uk.
You can find National Statistics on the internet on the Gov.uk website.
4. Background and methodology
4.1. Background
Soil nutrient balances provide a method for estimating the nutrient loadings of nitrogen and phosphorus to managed agricultural soils. Whilst a shortage of nutrients can limit the productivity of agricultural soils, a surplus of these nutrients poses a serious environmental risk. Losses of nutrients to the environment can impact on air quality (ammonia emissions), water quality (nitrate and phosphate levels in rivers) and climate change (nitrous oxide emissions). A soil nutrient balance estimate, expressed as a loading of nitrogen or phosphorus per hectare of managed agricultural land can be used as an indicator of the environmental risks. It provides a high level measure which can be used to monitor long term trends and to make meaningful comparisons between countries.
4.2. Methodology
A methodology for calculating soil nutrient balances has been developed by OECD (Organisation for Economic Cooperation and Development) and adopted by Eurostat (Statistical body of the European Commission). Although based on an internationally recognised methodology, the nutrient balance estimates are subject to a level of uncertainty or error margins. The approach estimates the full range of nutrient inputs and removals to soils from all sources. The input sources are: manures, mineral fertilisers, atmospheric deposition and biological fixation. The removals sources are: crop production and fodder production for livestock, including grazing. The nutrient input or removal from each source is either estimated directly (atmospheric deposition) or calculated by applying a coefficient (e.g. for the amount of nitrogen that a dairy cow produces each year) to the corresponding physical data characteristic (e.g. number of dairy cows). The relevant coefficients are derived from research and the physical data is taken from a wide range of data sources many of which are already published as official statistics.
4.3. UK approach
The estimates within this release are based on a programme of work to develop and improve the methodology and data sources. This work includes two funded projects and follow-up work carried out within Defra. Follow-up work is presented in a separate paper that gives an overview of the methods utilised to compile the data series within this release. The paper also gives details of where they differ to the proposals within the ADAS project and provides a commentary on the resultant balances and components. The project report can be found on the archive website. The estimates presented in this Statistics Notice use the June Survey data for England for commercial holdings for 2009 onwards and for all farms for preceding years. A consistent time series can be found in the accompanying excel worksheets. Managed agricultural land has been defined as the utilised agricultural area (UAA) excluding common land and sole right rough grazing. The balance per hectare is based on the area of managed agricultural land. This is based on the approximation that this is the only land to which significant levels of fertilisers and manures are applied.
4.4. Future publications
The next publication is due in July 2022
5. Glossary
Term | Definition |
---|---|
Nutrients | The key macro-nutrients required for crop growth which are nitrogen and phosphorus |
Inputs | The total amount of inputs of each nutrient to the soil. This can be through application of mineral fertilisers or organic manures, atmospheric deposition or biological fixation |
Offtake | The total amount of nutrients removed from the soil by the growth of crops, which are either harvested or grazed by livestock. |
Nutrient balance | The difference between the inputs and the offtake for each nutrient |
Loading | Another term for the balance, conveying that this is the total net amount being loaded onto the soil over a year |
Surplus | If the annual inputs exceed the offtake the net balance represents a surplus of the nutrient. This surplus represents an environmental risk as it can be lost from the soil to the air or water courses. |
Deficit | If the annual inputs are less than the offtake the net balance represents a deficit of the nutrient and hence the crop growth requirements will not have been met. |
Atmospheric Deposition | The process by which nitrogen in the atmosphere is transferred into soils. |
Biological Fixation | The process by which nitrogen in the atmosphere is incorporated into the tissues of plants and crops |