Ammonia emissions – what’s the problem?
Ammonia emissions are an environmental burden and a loss of valuable nitrogen for plant growth. Mitigating ammonia losses from fertiliser application thus provides a double benefit.
What exactly are the causes and consequences of ammonia volatilisation?
- Ammonia is a highly reactive, pungent gas formed of nitrogen and hydrogen. Its chemical formula is NH3. Ammonia occurs in essential biological processes and is not a problem in low concentrations. However, ammonia volatilisation into the atmosphere has negative consequences for agriculture, ecosystems and human health.
- Ammonia volatilisation from agricultural land is a loss of nitrogen for plant growth. It therefore comes at a cost for the farmer that needs to be minimized.
- Ammonia reacts with air humidity to form ammonium (NH4). Ammonium depositions contribute to acidification of land and water.
- Deposition of ammonium degrades the biochemistry of natural ecosystems and causes eutrophication (i.e. excess nutrient supply leading to e.g. algae proliferation).
- Ammonia combines with other air pollutants such as sulfuric acid and nitric acid to form secondary particulate matter (PM10). It stays in the air over several days and travels long distances. Particulate matter contributes to respiratory diseases.
Ammonia pollution from agriculture represents a high cost to society. According to the European Nitrogen Assessment, it is estimated at 12 € per kg of emitted nitrogen for health damages and 2 € for ecosystem damages.
Where does it come from?
94 % of all ammonia emissions in the EU result from agriculture. The remaining 6 % come from waste handling, road transportation and industrial applications.
Animal husbandry and manure
Livestock excreta contain high amounts of ammonia. They are at the origin of 75 % of all ammonia emissions from agriculture in the EU (figure 1). Emissions from livestock can be reduced but are beyond the scope here which is focused to mineral fertiliser.
Mineral fertiliser application accounts for 22 % of all ammonia emissions from agriculture in the EU (figure 1). These emissions are due to the transformation of ammonium solved in the soil to gaseous ammonia. The rate of transformation depends on the soil pH level. The higher the soil pH level, the more ammonium is converted to ammonia. The higher the temperature, the more ammonia is then lost to the atmosphere.
Mineral nitrogen fertilisers either directly contain ammonium (ammonium sulphate, ammonium sulfate nitrate, ammonium nitrate, CAN) or are converted to ammonium in the soil subsequent to spreading (urea and UAN). Urea and ammonium containing fertilisers are therefore subject to potential ammonia losses. Urea, however, is specifically prone to ammonia volatilisation (figure 3).
The case of urea hydrolysis of urea to ammonium temporarily increases the pH level in the direct vicinity of the application location. The increased pH level spurs the formation of ammonia, even on acidic soils (figure 2).
With temperatures above 15 °C, urea hydrolysis is fast and local ammonia concentrations in the soil rise, and thus volatilisation. Temperatures below 8 °C slow down the transformation of urea to ammonia, but also the subsequent nitrification of ammonia to nitrate, leading again to high ammonia concentrations and volatilisation.
Dry conditions reduce diffusion of ammonia in the soil and therefore also increase volatilisation. Rainfall after application, in contrast, reduces volatilisation. Field trials conducted in different European regions have demonstrated average
Comparing mineral fertilisers
Figure 4 summarizes the estimated ammonia volatilisation from different fertiliser types. CAN and AN offer the lowest emission factors of all nitrogen fertilisers.
Table 1 shows the ammonia emissions from main mineral fertilisers according to the emission factors defined by the European Environmental Agency. Urea (53.7 %) and UAN (18.4 %) together account for 72 % of these emissions, while CAN and AN amount for only 2,9 and 4,6 % respectively.
New NEC directive: what does it say?
Air pollution travels long distances and does not stop at national boundaries. It affects health of the most vulnerable and is responsible for acidification and eutrophication. What does Europe do to tackle the problem?
Setting emission ceilings
The European Union has put legislation in place to control air pollution. In 2001, the NEC (National Emission Ceilings) directive has set emissions ceilings per country for main pollutants (see table 1). In 2016, the NEC directive sets additional reduction targets per country.
The reference for the reductions to be achieved at the horizon of 2020 and 2030 are calculated based on actual emissions recorded in 2005 (figure 5).
The current status and the goals set out by the NEC directive are summarized in table 2.
It is worth noting that in some countries (e. g. France) ammonia emissions have increased since 2005 due to the extensive use of urea and UAN.
Best fertiliser practice
Ammonia emissions from fertiliser application can be significantly reduced. Each kg of nitrogen kept in the soil increases nitrogen efficiency and plant uptake. What are the practical measures to put in place?
Nitrogen forms make a difference
Ammonia from urea?
More than 72 % of ammonia emissions from fertiliser application are caused by urea and UAN. Ammonium nitrate generates 90 % less ammonia emissions per unit of nitrogen than urea. Replacing all urea and UAN by ammonium nitrate could save 63 % of overall ammonia losses from fertiliser application in Europe. With a potential emission reduction of about 470 kt NH3, this is the single most efficient measure to reduce ammonia volatilisation. When volatilisation risk is high, only CAN or AN shall be used.
Urease inhibitors slow hydrolysis of urea. More time therefore is available for diffusion into the soil, reducing ammonia concentrations and increasing the soil volume available for buffering pH.
Urease inhibitors can mitigate ammonia losses from urea by about 70 % and from UAN by about 40 %. For this reason the new German fertilizer ordinance requires either use of urease inhibitors or incorporation of urea when urea is applied from 2020 on. However, ammonia emissions still remain more than 3 times higher then those from CAN/ AN.
Urease inhibitors can improve environmental and agronomic outcome but do not overcome other weak points of urea such as lower spreading accuracy and lower reliability. Furthermore, degradation of the inhibitor on urea bears the risk of much lower ammonia emission control than claimed.
Applying fertiliser optimally
Incorporation upon spreading
Incorporation of urea into the soil immediately upon spreading, either by closed-slot injection or by cultivation, reduces potential volatilisation losses by up to 70 %. However, also in this case, ammonia emissions still remain more than 3 times higher than those from CAN/AN. Depth of injection and soil texture influence reduction efficiency.
Spreading urea under hot and windy conditions with no rainfall expected upon spreading shall be avoided. With dry soils, diffusion of ammonium and urea in the soil is slow and volatilisation losses are high.
Humid soils improve diffusion. Rainfall upon fertilizer application significantly reduces ammonia emissions by better distribution of fertilizer in the soil and mitigation of pH peaks.
Cool weather (< 15 °C) curbs formation of ammonia in the soil and subsequent volatilisation losses from urea. However, low temperatures often observed in early spring slow down the nitrification process. More ammonia thus remains in the soil, again increasing potential volatilisation losses.
Alkaline soils (high pH) result in higher volatilisation losses. Urea and UAN therefore shall not be spread on such soils.
Split application reduces ammonia concentrations and volatilisations risks.
Use of nitrate-based fertilisers and split application are the most efficient means to mitigate ammonia losses to the atmosphere.
Urease inhibitors reduce ammonia volatilisation from urea but remain less performant than ammonium nitrate.
Nitrogen compounds at a glance
a pungent smelling gas and air pollutant causing soil acidification, eutrophication, ground level ozone and a precursor of secondary particulate matter.
a cation found in low concentration in soil solution and fixed by clay mineral.
an anion found in the soil solution. Preferred nitrogen form taken up by plants.
N2O Laughing gas:
a 300 times more powerful greenhouse gas than CO2.
NOx Nitrous oxides:
an abbreviation designating both, NO and NO2. Important air pollutant causing ground level ozone and a precursor of secondary particulate matter.
an unreactive gas that is abundant in the atmosphere
 Brink C, van Grinsven H (2011): Cost and benefits of nitrogen in the environment. The European Nitrogen Assessment, chapter 22, Cambridge University Press
 Bouwman A F, Boumans L J M, Batjes N H (2002): Estimation of global NH3 volatilization from mineral fertilizer and animal manure applied to arable land and grasslands, Global Biochemical Cycles, 16, 1-15
 Hutchings N, Webb J, Amon B (2016): EMEP/EEA air pollutant emission inventory guidebook
 Bittman S, Dedina M, Howard CM, Oenema O, Sutton MA (2014): Options for Ammonia Mitigation. Guidance from the UNECE Task Force on Reactive Nitrogen, chapter 8, Centre for Ecology and Hydrology, Edinburgh, UK