Driving forces and impacts of food system nitrogen flows in China, 1990 to 2012
- 1. Xiamen Key Lab of Urban Metabolism, Xiamen 361021 (China)
- 2. Key Lab of Urban Environment and Health, Institute of Urban Environment, Chinese Academy of Sciences, Xiamen 361021 (China)
- 3. School of Biotechnology Engineering, Jimei University, Xiamen, 361021 (China)
- 4. Fenner School of Environment and Society, Australian National University, Canberra 0200 (Australia)
Description
Highlights: • Urban-rural difference in per capita plant- and animal-food N (AN) was studied. • One demands 0.3–0.5 kg more AN yr− 1 when he moved to cities from a rural area. • 17% increased AN was caused by rural-urban migration between 1990 and 2012. • Dietary changes no significant contribution to N increase over the past two decades. • Urban food-sourced N losses to soil and water bodies are 3 folds of rural area. Food nitrogen (N), which includes animal-food (AN) and plant-food N (PN), has been driven by population growth (PG), dietary changes associated with income growth (DC) and rural-urban migration (M) over the past three decades, and these changes combined with their N cost, have caused some effect on N use in China's food system. Although there is an increasing literature on food N and its environmental impacts in China, the relative magnitude of these driving forces are not well understood. Here we first quantify the differences in per capita AN and PN consumption in urban and rural areas and their impacts on N input to the food system during 1990–2012, and then quantify the relative contributions of DC, PG and M in the overall N change during this period. Our results show that a resident registered as living in city required 0.5 kg more AN yr− 1 and 0.5 kg less PN yr− 1 than one living in a rural area, in 2012. DC, PG and M accounted for 52%, 31% and 17% of the total AN increase, respectively. These three factors caused 46% of the increased N use for food production over the past two decades. Another 54% was mainly caused by the declining in N use efficiencies of the food system. Food-sourced N loss intensity in urban and rural areas were 502 and 162 kg N hm− 2 in 2012, a three-fold difference due to the increasing amount and a linear rural-urban flow of N input, and inadequate N recovery via solid waste and wastewater treatment in cities. Our study highlights China is facing higher risks of environmental N pollution with urbanization, because of the high demand for AN and higher food-sourced N loss intensity in urban than in rural areas.
Availability note (English)
Available from http://dx.doi.org/10.1016/j.scitotenv.2017.08.071Additional details
Identifiers
- DOI
- 10.1016/j.scitotenv.2017.08.071;
- PII
- S0048969717320697;
Publishing Information
- Journal Title
- Science of the Total Environment
- Journal Volume
- 610
- Journal Page Range
- p. 430-441
- ISSN
- 0048-9697
- CODEN
- STENDL
INIS
- Country of Publication
- Netherlands
- Country of Input or Organization
- International Atomic Energy Agency (IAEA)
- INIS RN
- 54105955
- Subject category
- S54: ENVIRONMENTAL SCIENCES;
- Descriptors DEI
- ANIMALS; CHINA; FOOD CHAINS; HAZARDS; MATERIALS RECOVERY; NITROGEN; PLANTS; POLLUTION; RURAL AREAS; SOILS; SOLID WASTES; URBAN AREAS; WASTE WATER; WATER TREATMENT
- Descriptors DEC
- ASIA; ELEMENTS; HYDROGEN COMPOUNDS; LIQUID WASTES; MANAGEMENT; NONMETALS; OXYGEN COMPOUNDS; PROCESSING; WASTE MANAGEMENT; WASTE PROCESSING; WASTES; WATER
Optional Information
- Copyright
- Copyright (c) 2017 The Authors. Published by Elsevier B.V.