Abstract

This study presents the first detailed estimate of Rwanda’s nitrogen (N) flows and N footprint for food (NFfood) from 1961 to 2018. Low N fertilizer inputs, substandard production techniques, and inefficient agricultural management practices are focal causes of low crop yields, environmental pollution, and food insecurity. We therefore assessed the N budget, N use efficiency (NUE), virtual N factors (VNFs), soil N mining factors (SNMFs), and N footprint for the agro-food systems of Rwanda with consideration of scenarios of fertilized and unfertilized farms. The total N input to croplands increased from 14.6 kg N ha−1 yr−1 (1960s) to 34.1 kg N ha−1 yr−1 (2010–2018), while the total crop N uptake increased from 18 kg N ha−1yr−1 (1960s) to 28.2 kg N ha−1yr−1 (2010–2018), reflecting a decline of NUE from 124% (1960s) to 85% (2010–2018). Gaseous N losses of NH3, N2O, and NO increased from 0.45 (NH3), 0.03 (N2O), and 0.00 (NO) Gg N yr−1 (1960s) to 6.98 (NH3), 0.58 (N2O), and 0.10 (NO) Gg N yr−1 (2010–2018). Due to the low N inputs, SNMFs were in the range of 0.00 and 2.99 and the rice production, cash-crop production, and livestock production systems have greater SNMFs in Rwanda. The weighted NFfood per capita that presents the actual situation of fertilized and unfertilized croplands increased from 4.0 kg N cap−1 yr−1 (1960s) to 6.3 kg N cap−1 yr−1 (2010–2018). The NFfood per capita would increase from 3.5 kg N cap−1 yr−1 to 4.8 kg N cap−1 yr−1 under a scenario of all croplands without N fertilizer application and increase from 6.0 to 8.7 kg N cap−1 yr−1 under the situation of all croplands receiving N fertilizer. The per capita agro-food production accounted for approximately 58% of the national NFfood. The present study indicates that Rwanda is currently suffering from low N inputs, high soil N depletion, food insecurity, and environmental N losses. Therefore, suggesting that the implementation of N management policies of increasing agricultural N inputs and rehabilitating the degraded soils with organic amendments of human and animal waste needs to be carefully considered in Rwanda.

Highlights

  • By 2050, the world’s population is projected to reach 9.7 billion, with the populations of Sub-Saharan Africa (SSA) being doubled (United Nations, 2019)

  • We developed soil N mining factors (SNMFs) based on the following equation (Hutton et al, 2017) to quantify N coming from soil mining but not considered in the N footprint for food (NFfood) calculation: N input from soil stocks

  • 3.1 Sources of N Inputs In Rwanda, the total N input (TNI) to croplands increased from 9.0 Gg N yr−1 (14.6 kg N ha−1yr−1) during the 1960s to 47.8 Gg N yr−1 (34.2 kg N ha−1yr−1) during 2010–2018 (Figure 1)

Read more

Summary

Introduction

By 2050, the world’s population is projected to reach 9.7 billion, with the populations of Sub-Saharan Africa (SSA) being doubled (United Nations, 2019). The rapid growth of the world population demands increasing food demand and production (Katz, 2020). These demands of agro-food products require a highly productive agroecosystems with high inputs of fertilizers, nitrogen (N) fertilizers. It should be noted that worldwide, synthetic N fertilizers (SNF) are not distributed and there are large differences in SNF use between the African continent and the other continents (Raza et al, 2018). Excess N applied to arable lands, with low N use efficiency (NUE), has caused several issues, such as soil degradation, water pollution, and greenhouse gas emissions (Spiertz, 2009)

Objectives
Methods
Results
Discussion
Conclusion
Full Text
Published version (Free)

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call