A nitrogen footprint model to help consumers understand their role in nitrogen losses to the environment

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Abstract

The human use of reactive nitrogen (Nr) in the environment has profound beneficial and detrimental impacts on all people. Its beneficial impacts result from food production and industrial application. The detrimental impacts occur because most of the Nr used in food production and the entire amount of Nr formed during fossil fuel combustion are lost to the environment where it causes a cascade of environmental changes that negatively impact both people and ecosystems.

We developed a tool called N-Calculator, a nitrogen footprint model that provides information on how individual and collective action can result in the loss of Nr to the environment. The N-Calculator focuses on food and energy consumption, using average per capita data for a country. When an individual uses the N-Calculator, the country average is scaled based on the individual's answers to questions about resource consumption.

N footprints were calculated for the United States and the Netherlands, which were found to be 41 kg N/capita/yr and 24 kg N/capita/yr, respectively. For both countries, the food portion of the footprint is the largest, and the food production N footprints are greater than the food consumption N footprints.

The overarching message from the N-Calculator is that our lifestyle choices, and especially our food consumption, have major impacts on the Nr losses to the environment. Communicating this message to all of the stakeholders (the public, policymakers, and governments) through tools like the N-Calculator will help reduce Nr losses to the environment.

Highlights

► Developed personal nitrogen footprint model, the N-Calculator. ► N-Calculator links personal resource consumption to nitrogen losses to environment. ► Nitrogen footprint includes food consumption/production and energy usage. ► US and Netherlands nitrogen footprints are 41 and 24 kg N/capita/yr, respectively. ► Food, and especially food production, make up largest part of nitrogen footprint.

Introduction

The human use of reactive nitrogen (Nr, all nitrogen species except N2) in the environment has profound beneficial and detrimental impacts on all people. Agricultural uses, including both food production and consumption, contribute the most Nr to the global environment; the burning of fossil fuels is the next biggest contributor. The beneficial impacts of the agricultural use of Nr are related to food production using nitrogen fertilizer and human-enhanced biological nitrogen fixation. These two processes provide the Nr to sustain about half of the world's population (Erisman et al., 2008). The detrimental impacts result because most of the Nr used in food production and the entire amount of Nr formed during fossil fuel combustion are lost to the environment.

Once lost to the environment, the nitrogen moves through the Earth's atmosphere, forests, grasslands, and waters causing a cascade of environmental changes that negatively impact both people and ecosystems. These changes include smog, acid rain, forest dieback, coastal ‘dead zones’, biodiversity loss, stratospheric ozone depletion, and an enhanced greenhouse effect (Galloway et al., 2003, Galloway et al., 2008). The disruption of the N cycle and its impacts necessitate measures to optimize food production and energy use while minimizing the effects. Therefore policies, measures, and behavioral changes are essential. Here we describe tools that can support policymakers, stakeholders, producers, and consumers in that process.

Of all the chemical elements, nitrogen is one whose abundance has been increased the most by human activity (Erisman et al., 2008). Globally, humans contribute about twice the amount of nitrogen to the environment as do all the natural terrestrial processes; on a regional basis it can be many-fold more (e.g., US, 5-fold (United States Environmental Protection Agency, 2011); Europe, 4-fold (Sutton et al., 2011)). In contrast, human activity contributes 5–10% of CO2 emissions; natural processes contribute the remainder (Le Quéré, 2010).

Over the past decade, there have been significant advances in our scientific understanding of the magnitude and consequences of the human alteration of the nitrogen cycle. With these scientific advances, and a much better understanding of how to decrease the negative impacts of nitrogen without impacting the ability to produce food and use energy, we feel it is appropriate to address the challenge of communication and to help consumers and policymakers minimize their role in the disruption of the N cycle and the resulting environmental consequences. We plan to do this by means of a collection of tools brought together in a system called N-PRINT (Fig. 1). Ultimately, N-PRINT will be able to describe how Nr is lost to the environment and its resulting impacts due to individual (consumer) and collective (producers and society) consumption behavior and the ways in which policy can have an effect on these losses.

In this paper we will focus on the N-Calculator, which is a per capita N footprint model that defines an N footprint as the total amount of Nr that is lost to the environment due to individual's consumption of food and energy. The N-Calculator provides an integrated approach that takes into account not only the food and energy consumed by individuals, but also the “up-stream” processes that release Nr to the environment by virtue of the production of the food, energy, goods, and services that individuals use.

The ‘footprint’ concept has been developed over the last decade to serve as a metric of the single or collective impacts of people on the environment, relative to the capacity of the planet to support those people. There are a number of existing footprint calculators, with The Ecological Footprint being one of the earliest and the most well known with components like energy, food and fiber, timber and paper, and built-up land (Wackernagel et al., 1999, Wackernagel et al., 2002, Global Footprint Network, 2011).

Several groups have examined Nr flows associated with the use of food and energy by people and regions (e.g., cities, nations). For example, the Chesapeake Bay Foundation in the US has a calculator (Chesapeake Bay Foundation: Your Bay Footprint, 2011) that estimates a household's contribution to Nr inputs to the Bay resulting from energy use, sewage production, and lawn fertilizer usage. A much more specific calculator has been prepared to estimate N, C, and P fluxes in 360 household ecosystems in the Minneapolis-Saint Paul, Minnesota (USA) urban region. Fissore et al. (2011) found that Nr fluxes into the households were dominated by human diet, lawn fertilizer applications and surface transportation, which together accounted for ∼85% of total household Nr inputs.

In a life-cycle analysis Xue and Landis (2010) examined the N and P eutrophication potential of food consumption patterns. They showed that different food groups exhibit a highly variable nitrogen-intensity. On average, red meat and dairy products require much more nitrogen than cereals/carbohydrates. An important point they make is that the ranking of foods' nitrogen footprints is not consistent with their carbon footprints. For example, dairy products and chicken/eggs have high nitrogen footprints but low carbon footprints.

Most recently, Galli et al. (2011) have clustered a suite of indicators (ecological, carbon, water; the “Footprint Family”) to track human pressure on the planet. The work was developed under the One Planet Economy Network: Europe (OPEN:EU) project, funded by the 7th Framework Program in the European Commission, and builds on the premise that no single indicator per se is able to comprehensively monitor human impact on the environment, but indicators rather need to be used and interpreted jointly. As they note in the paper, to better track the environmental impacts of production and consumption activities and assess tradeoffs, the Footprint Family could thus benefit from the inclusion in the suite of additional footprint-type of indicators such as ‘nitrogen’. In that regard, one of the objectives of this paper is to provide the methodology behind the nitrogen footprint to make it easier to integrate into the Footprint Family.

The objectives of this paper are (1) to provide background on the scientific approaches in model development and explain the methodology of the N-Calculator and (2) to present the nitrogen footprint of the United States and the Netherlands.

Section snippets

Average per capita country nitrogen footprints

We define a nitrogen footprint as the total amount of Nr released to the environment as a result of an entity's resource consumption, expressed in total units of Nr. The N-Calculator focuses on four main areas of consumption: food, housing, transportation, and goods and services. The N footprint consists of the N embodied in food consumption and production as well as the NOx emitted by fossil fuel combustion. The N footprint of each of the areas of consumption is calculated using average per

Results

N-Calculators have been completed with data for the United States and the Netherlands. The N-Calculator found that the average per capita N footprint in the United States is 41 kg N/yr and in the Netherlands is 25 kg N/yr (Fig. 5). For the per capita US footprint, food production accounts for 30 kg N/yr, of which 25 kg N/yr is lost to the environment prior to food consumption (e.g. during food production), and 5 kg N/yr is lost to the environment after food consumption (e.g. as human waste). For the per

Average per capita country nitrogen footprints

The substantial difference between the US (41 kg N/capita/yr) and Netherlands (25 kg N/capita/yr) N footprints can be attributed to a variety of reasons across the sectors. In general, both the consumption of resources and the production losses are lower in the Netherlands than in the US.

Conclusions

Over the past few years, several footprint approaches have been developed for water, carbon, and for the ecological effects of human consumption. Here we present the first N footprint calculator. The disruption of the regional to global N cycle and its consequences is not well known to the public and to policymakers. Furthermore, because of the complexity of the issue there is only limited knowledge about how to optimize the increasing need for food and energy while limiting the effects of Nr

Role of the funding source

This study was supported with funding from a variety of sources. We appreciate the assistance we have received from the Agouron Institute, the Energy Research Center of the Netherlands, the Tyler Foundation, the United States Environmental Protection Agency, the Netherlands Ministry of Infrastructure and the Environment, and the University of Virginia. These sponsors have not played a role in the study design, the data, the report, or the decision to submit a paper for publication.

Acknowledgments

This paper is a contribution to the International Nitrogen Initiative. A topic of this breadth required intellectual support from many individuals, and we are very thankful to the following for their important input: Dale Allen, Robert Bastian, Marshall Burke, Russell Dickerson, Otto Doering, Rick Haeuber, Arjan Hensen, Brendan McLaughlin, Bill Moomaw, Harold Mooney, Carolyn Opio, Nicolas Sakoff, Kaj Sanders, Henning Steinfeld, Thomas Theis, and Penelope Whitney.

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