Anthropogenic release of reactive nitrogen (Nr; all species of N except N2) to the global nitrogen (N) cycle is substantial and it negatively affects human and ecosystem health. A novel metric, the N footprint, provides a consumer-based perspective for Nr use efficiency and connects lifestyle choices with Nr losses. Here we report the first full-scale assessment of the anthropogenic Nr loss by Australians. Despite its ‘clean and green’ image, Australia has the largest N footprint (47 kg N cap−1 yr−1) both in food and energy sectors among all countries that have used the N-Calculator model. About 69% of the Australia’s N footprint is attributed to food consumption and the associated food production, with the rest from energy consumption. Beef consumption and production is the major contributor of the high food N footprint, while the heavy dependence on coal for electricity explains the large energy N footprint. Our study demonstrates opportunities for managing Nr loss and lifestyle choices to reduce the N footprint.
More than half of the world’s population is nourished by food produced using synthetic nitrogen (N) fertilizers1,2. However, N escapes to the environment as reactive N (Nr; all species of N except N2) through different pathways during food and energy production and consumption3,4. With a large anthropogenic Nr creation rate and continued losses of Nr through human activities, increasing amounts of Nr are accumulating in the environment where they contribute to negative impacts. For example, the Nr-related damage in the European Union (EU) has been estimated at €70 billion to €320 billion per year5.
The N footprint is an index that assesses the total amount of Nr released to the environment as a result of an entity’s resource consumption6. It includes Nr losses from food production, food consumption, fossil fuel combustion for housing and transportation, and provision of goods and services. Using the N-Calculator model, the N footprint has been developed for many countries (i.e., United States, Netherlands, Germany, United Kingdom, Japan, Austria)6,7,8,9,10,11. This consumer-based tool can connect individual consumption choices with Nr losses and show how lifestyle choices affect these Nr losses. Using a different approach (a mass balance), N footprints have also been calculated in other countries such as China12. A Multi-Region Input-Output (MRIO) approach, which accounts for trade by tracking N losses through economic models, was used to calculate the N footprint for 188 countries13. However, compared to the N-Calculator, these approaches have less focus on consumers’ behavior.
While Australia and its products are often perceived as being ‘clean and green,’14 it has unique challenges for managing Nr issues. Although Australia is the planet’s sixth largest country, it has a small population (24 million) with a low population density of 3 people/km2 compared to the global average of 49 people/km2 (ref. 15). However, 85% of Australia’s population is found in the coastal areas, resulting in higher environmental risk to the coastal habitats (e.g., Great Barrier Reef)16. Furthermore, more than half of Australia’s land is used for farming production, 90% of which is used for grazing in the arid and semi-arid zones17. The widespread use of agricultural land in Australia has led to issues such as mining soil N in dryland rain-fed wheat systems and excessive N use in feedlot animal production systems18,19. Although numerous studies have linked agricultural Nr to environmental problems20,21,22, the N footprint has not been quantified for Australia. The objectives of our study were therefore to: (1) assess the Nr loss driven by food and energy consumption and associated production in Australia using the N-Calculator model; (2) benchmark Australia’s performance of Nr loss against other countries; and (3) explore the driving forces and mitigation strategies for the Australia’s N footprint.
Per capita N footprint in Australia
The per capita N footprint in Australia was 47 kg N yr−1 in 2011. The food portion of the N footprint (32 kg N capita−1 yr−1) was the largest component, of which 2 kg N capita−1 yr−1 was from food consumption after sewage treatment and 30 kg N capita−1 yr−1 from the associated food production. However, before being corrected for the amount of Nr converted to N2 or recycled during sewage treatment, the actual food consumption N was 5 kg N capita−1 yr−1 (Fig. 1a, Supplementary Table 1). 82% of the food N footprint is from animal products, half of which is from beef (Fig. 1b). For crop products, cereals represent the largest proportion (35% of the crop N footprint), followed by vegetables, potatoes, fruits and legumes (Fig. 1b). The energy sectors contribute 15 kg N capita−1 yr−1, which is made up of the housing (9 kg N capita−1 yr−1), transportation (2 kg N capita−1 yr−1), and goods and services (4 kg N capita−1 yr−1) sectors (Fig. 1a, Supplementary Table 1). Almost half of the energy N footprint comes from electricity consumption (Fig. 1c).
Australia’s virtual N factors (VNFs)
There is a large variability in Australia’s VNFs (a metric that describes the total Nr loss to the environment during food production per unit of N in the consumed food product6), which range from 1.2 (legumes) to 29.8 (feedlot lamb) kg N released to the environment per kg N consumed (Table 1, Fig. 2, Supplementary Table 4). Generally, animal products’ VNFs are larger than those of plant products. For plant products, the VNF is as low as 1.2 (legumes) and 1.8 (cereals), and as high as 8.0 (vegetables) and 9.4 (fruits). The VNF of animal products ranges from 0.6 for wild-caught seafood to 25.2 and 29.8 for feedlot beef and lamb respectively; other meat products have a VNF of around 5 (Table 1, Fig. 2, Supplementary Table 4). Production methods affect the VNFs. Examples include wild-caught seafood (0.6) vs. farmed seafood (4.2), lamb from the grazing system (5.7) vs. feedlot system (29.8), and beef from grazing system (7.4) vs. feedlot system (25.2) (Fig. 2b, Supplementary Table 4). Australia’s feedlot production systems have a higher VNF than grazing production systems (Fig. 3). Although most of Australia’s sheep and cattle by count are grazing outdoors, the feedlot systems contribute a large percentage of meat production. The Australian beef and lamb VNFs weighted by production are still higher than those of other countries.
Australia vs. other countries
At a global scale, Australia has the largest N footprint both in the food and energy sectors among the nine countries where the N footprint has been calculated using the N-Calculator model (Fig. 1a, Supplementary Table 1). Australia’s food N footprint is the largest because it has the highest rate of beef consumption and the highest beef VNF (Fig. 1a, Table 1, Supplementary Table 1). The food N footprint is the largest component of the total N footprint among all of the countries (69–92% of the total N footprint), and the amount of Nr loss associated with food production is the highest in Australia (30 kg N capita−1 yr−1). The amount of N consumed as food in Australia (5 kg N capita−1 yr−1) is similar to that in other developed countries (5–6 kg N capita−1 yr−1) but higher than that in less-developed countries (Tanzania; 2 kg N capita−1 yr−1). However, Australia and most of the developed countries use advanced wastewater treatment to recycle or convert Nr to N2, which substantially diminishes the discharge of Nr from food consumption to the environment (e.g. the Nr removal factor is 60% in Australia, 79% in Austria, 78% in the Netherlands, and 67% in Germany).
For the energy sectors, Australia has the highest total energy N footprint (15 kg N capita−1 yr−1) among all countries, which is several times higher than the Netherlands, Austria, Japan, and Germany (2–4 kg N capita−1 yr−1) and even tenfold higher than Tanzania (1 kg N capita−1 yr−1) (Fig. 1a, Supplementary Table 1). Australia’s energy N footprint is the largest due to a heavy dependence on coal, which drives up its electricity N footprint.
The VNFs, which represent the Nr losses along the food production chain, vary substantially with food types6. In most countries, production of legumes and seafood is the most efficient while the production of beef is the least efficient in terms of Nr use6,7,8,9,23 (Table 1, Supplementary Table 4). Although vegetables and fruits have large VNFs because of low N use efficiency in these production systems24,25, the Nr loss per serving of vegetables or fruits is low due to the very low N content compared to other food types9. Beef production is the least efficient way of using N and supplying dietary protein in most countries that have completed their calculation of VNFs6,7,8,9,23, mainly due to the large feed requirements and their high basal metabolic rate26. An analysis of the environmental impacts of the various livestock categories in the United States had a consistent finding6,8,27. Eshel et al.27 demonstrated that in addition to higher Nr losses, per consumed calorie of beef also required more land and irrigation water and released more GHG than the other livestock products.
The VNFs also vary significantly across nations due to different food production methods. Australia has lower VNFs than Japan but higher VNFs than other countries that have completed this calculation (Table 1). The key variables that affect these results are the fertilizer N use efficiency for crops and the feed N conversion ratio for animals. For instance, the portion of N uptake from fertilizer by cereals is 80% in the US and 43% in Japan, and the portion of N retained in feedlot cattle is 20% in the US and 14% in Japan6,8. The Australian value for N uptake from fertilizer by cereals (77%) is comparable to the US but much higher than Japan, whereas the value for N retained in feedlot cattle (14%) is the same as Japan, but much lower than the US. These values drive the VNFs and suggest that less Nr is released from cereal production in Australia than in Japan, but more Nr from feedlot beef production in Australia than in the US. However, VNF calculation looks just at the Nr loss during production and does not connect to environmental impacts. Because of the extensive grazing in Australia, the high Nr losses from beef could be diluted by the extensive space and arid climate.
According to the Australia’s Dietary Guidelines (ADGs), the recommended consumption of high protein food (lean meat, fish, and eggs) is 200–300 g capita−1 day−1 (for the age group 19–50 years), but the actual consumption level is double28,29. Meanwhile, the actual consumption of cereals (240 g capita−1 day−1) is much lower than the recommended amount of 600 g capita−1 day−1 (ref. 29). The required annual N intake as protein is 2.5–3.5 kg N capita−1 based on the WHO30 and USDA31 dietary recommendation, but Australians consume 5.0 kg N capita−1 yr−1 (Fig. 1a, Supplementary Table 1). 72% of N consumption in Australia is from animal food (Table 1), and beef is the main contributor. Beef consumption by Australia’s people is more than double and four times larger than the consumption by the British and the Japanese, respectively (Table 1). The high consumption level and high VNF of beef resulted in Australia having the largest beef N footprint (11.1 kg N capita−1), which is much greater than that in other countries (Table 1). As studies have shown how food choices and diet changes can reduce the Nr emission in the European Union32,33, choosing a diet better aligned with the Australia dietary guidelines would both reduce Australia’s N footprint and improve consumers’ health.
Australia has a large land area with low rainfall and fertility, both of which promote the long tradition of grazing cattle. About 97–98% of 28 million cattle in Australia are located in extensive native grasslands34, which receive little or no fertilizer N35. Although the N feed conversion ratio by feedlot cattle (14%)36 is higher than cattle in extensive grazing farms (7–10%)37,38, we found that 79% of N excreted by grazing cattle will return to the grassland whereas only 15% of N excreted from feedlot cattle will be collected and reused (Fig. 2b, Fig. 3, Supplementary Fig. 1, Supplementary Table 4). In particular, ammonia (NH3) emissions from the grazing system are estimated at 0.2 kg NH3-N/kg manure N39 but 0.81 kg NH3-N/kg manure N in the feedlots21,36. That means that when producing the same amount of beef, more Nr is released to the environment from feedlot systems than from grazing farms. Likewise, the comparisons between grazing versus feedlot lamb and wild-caught versus farmed seafood also indicate that the extensive food production systems in Australia release less Nr than the intensive ones (Fig. 2b, Supplementary Fig. 1, Supplementary Table 4). Around two thirds of total Australia’s agricultural products are exported worldwide with an international reputation for clean and green production40. In particular, the relatively mild climate enables livestock to graze year-round41, which supports protein-rich diets in Australia and helps to produce large exportable food surpluses (e.g., Australia is the second largest exporter of beef in the world)42.
Australia also has abundant energy resources. Due to the plentiful resources and low-cost production43, 69% of electricity was generated from coal during 2012–2013, which was higher than any other developed country (e.g., 43% in the US and 29% in the UK)44. We demonstrated that Australia emitted about 7.5 kg N capita−1 from electricity generation in 2011, compared to 3.7 and 1.8 kg N capita−1 for the US and the UK, respectively. The high N emissions associated with electricity generation concomitantly contributed to a larger N footprint for goods and services in Australia (Fig. 1a, Supplementary Table 1). The high transportation N footprint is caused by the low housing density and long distances of daily travel in Australia, as well as the less stringent regulations on energy efficiency, vehicle emissions and carbon pricing than other developed nations such as the US and the UK45. However, Australia has a rich diversity of renewable energy resources (wind, solar, geothermal, hydro, wave, tidal, bioenergy), the wide adoption of these renewable resources would decrease the energy component of the N footprint.
The unexpectedly large Australian N footprint has not been uncovered until now. Our results show that lifestyle choices (especially beef consumption and coal for electricity) have major impacts on Nr losses to the environment. Consumers could reduce their N footprint by choosing a diet with less meat and using more renewable energy. The on-farm N footprint can be reduced by improving farm N use efficiency, such as by the 10 “Key Actions” listed in “Our Nutrient World”46. These strategies are critical for meeting the increasing demand for food and energy in an environmentally sustainable way.
Materials and Methods
This consumer-based study accounts for the all domestic consumption and the associated production of food and energy in Australia. Given this consumer focus, this study does not account for the N footprint of exports. We also assumed that all food and energy were produced using Australia’s production methods and therefore did not account for the effects of imports. The N footprint was divided into food, housing, transportation and goods & services, and each sector was further divided into subsectors to cover the major human activities related to Nr loss.
N footprint calculation
For the food component of the N footprint, we estimated the Nr losses to the environment along the food production and consumption chain, starting with N fertilizer applied to cropland and ending with sewage treatment. The food N footprint has two parts: the food consumption N footprint and the associated food production N footprint. Food consumption was calculated by subtracting food waste from the Australia’s food supply28. The food consumption N was assumed to be completely excreted since adults generally do not accumulate N in their body47. Nonetheless, the widespread use of advanced sewage treatment in Australia removes 60% of this Nr from the sewage stream by either converting it into a non-reactive form (N2) or recycling and reusing it in the form of sludge48,49. The N removal from the sewage stream is considered a reduction to the food consumption N footprint.
The associated food production N footprint accounts for all N lost during the food production process. The food production N footprint is calculated using virtual N Factors (VNFs), which are defined as the total Nr loss to the environment during production per unit of N in the final consumed food products. Examples of these N losses include the fertilizer Nr not incorporated into the plant, feed Nr not retained in the animal products, crop residues Nr not recycled, and processing and food waste Nr6. Food production N is calculated by multiplying the VNF by the food N consumed; the VNFs covers all steps from initial fertilizer application to final food consumption. We calculated Australia’s VNFs for 12 major food categories: cereals (weighted-average of rice, wheat, barley, sorghum), legumes, potatoes, vegetables, fruits, seafood (weighted-average of wild-caught and farmed), poultry, egg, dairy products (weighted-average of milk, cheese, yoghurt and dry milk), pork, lamb and beef (weighted-average of grazing and feedlot systems) (see Supplementary Table 4, Supplementary Fig. 1 for Nr flow along the food production and consumption chain).
Nr losses associated with energy use during food production (e.g., on-farm energy use, food processing, packaging, transportation) were also included as part of the food N footprint. We used an environmentally extended input–output analysis (EEIO) to allocate Australia’s total NOx and NH3 emissions associated with food production to various food categories6,50.
The energy component of the N footprint consists of four main aspects of daily life associated with energy consumption: housing (e.g., electricity, natural gas use), transportation (e.g., plane, train, car), goods (e.g., clothing, furniture, tools) and services (e.g., education, insurance and financial services). A bottom-up approach was adopted to calculate the N footprint for major areas of N consumption (electricity, heating, personal travel). For these sectors, activity data (e.g. hours flown by aircraft) was used with an emission factor (e.g. amount of Nr emitted per hour flying) (see Supplementary Table 3 for data and references). A top-down approach (EEIO analysis for emissions of N from NOx and NH3 within Australia) was used to calculate the N footprint of the remaining sectors related to consumers6,50. After removing any double-counting of fuel sources, the sum of the bottom-up and top-down footprints is the total energy N footprint.
Key sources of data for the N footprint included: International statistical data sources; Australia’s governmental statistical data sources; industry data sources; data from a number of published articles for some coefficients; consultation with industry, researchers, and other experts in the field (Supplementary Tables 2, 3 and 4).
How to cite this article: Liang, X. et al. Beef and coal are key drivers of Australia’s high nitrogen footprint. Sci. Rep. 6, 39644; doi: 10.1038/srep39644 (2016).
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We thank Justin Kitzes for the environmentally extended input–output analysis and Drs N. Andy Cole, Julian Hill, Stephen Wiedemann, Des Rinehart for their advice on NUE of Australia’s livestock. We thank Drs Robert Norton, John Angus and Richard Eckard for comments of crop and pasture NUE. We thank Drs Murray Unkovich and DF Herridge for their suggestion of Australia’s N fixation. Authors also acknowledge the International Nitrogen Initiative (INI) for bringing attention to the N-Print project as an official activity, the University of Melbourne for the research Scholarship, the Meat and Livestock Australia, Discovery Early Career Researcher Award, The Australian Research Council (DE170100423), Australia-China Joint Research Centre – Healthy soils for sustainable food production and environmental quality for financial support.
The authors declare no competing financial interests.
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Liang, X., Leach, A., Galloway, J. et al. Beef and coal are key drivers of Australia’s high nitrogen footprint. Sci Rep 6, 39644 (2016). https://doi.org/10.1038/srep39644
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