Institute of Xilingol Bioengineering Research, Xilingol Vocational College, Xilinhot, 026000, China.
Key Laboratory of Geographic Information Science (Ministry of Education), School of Geographic Sciences, East China Normal University, Shanghai, 200241, China; Institute of Eco-Chongming (IEC), East China Normal University, Shanghai, 202162, China.
Environ Pollut. 2021 Jun 15;279:116906. doi: 10.1016/j.envpol.2021.116906. Epub 2021 Mar 10.
The release of reactive nitrogen (N) from food production and consumption constitute the primary source of nitrogen pollution. However, nitrogen flows and the driving factors of food chain of Shanghai, China have not been previously studied. Here, we used a substance flow analysis model to analyze the changes in N inputs and outputs in agricultural production, livestock and poultry farming, and food consumption related to the Shanghai food chain between 2000 and 2018. The driving forces of N inputs, N use efficiency, and N surpluses/deficits in the food production and consumption system were also investigated. The results indicated that the main sources of N input in the food production and consumption system were nitrogen fertilizers, livestock and poultry feed from external sources, and plant-based foods, which accounted for 36.28-59.45% of N input in agricultural production, 37.32-76.57% of N input in livestock and poultry farming, and 35.38-59.37% of N input in food consumption, respectively. The main forms of N outputs were surplus nitrogen in the soil, excretal nitrogen from livestock and poultry animals, and excretal nitrogen from humans, which accounted for 38.2-48.89% of N output in agricultural production, 36.78-55.18% of N output in livestock and poultry farming, and 85.36% of N output in food consumption, respectively. From 2000 to 2018, the N inputs per unit area from agricultural production decreased at a rate of 20.42% before 2012, and then increased at a rate of 5.72%. Moreover, the N use efficiency of agricultural production component of Shanghai was at a low level, only 18.43-27.6%. Cultivation area of crops was the main driving forces of the N input to food production and consumption system. These results provide essential data for controlling nitrogen pollution caused by Shanghai food production and consumption, which can serve as a reference for administrative agencies in formulating policies.
食物生产和消费过程中释放的活性氮(N)是氮污染的主要来源。然而,中国上海的食物链中氮流动和驱动因素尚未得到研究。在这里,我们使用物质流分析模型来分析 2000 年至 2018 年期间农业生产、畜牧业和食品消费相关的上海食物链中氮投入和产出的变化。还研究了食物生产和消费系统中氮投入、氮利用效率和氮盈余/亏缺的驱动因素。结果表明,食物生产和消费系统中氮投入的主要来源是化肥、外部来源的畜禽饲料和植物性食品,分别占农业生产氮投入的 36.28-59.45%、畜牧业氮投入的 37.32-76.57%和食品消费氮投入的 35.38-59.37%。氮输出的主要形式是土壤中剩余的氮、畜禽动物的排泄物氮和人类的排泄物氮,分别占农业生产氮输出的 38.2-48.89%、畜牧业氮输出的 36.78-55.18%和食品消费氮输出的 85.36%。2000 年至 2018 年期间,农业生产单位面积的氮投入以 20.42%的速度在 2012 年之前减少,然后以 5.72%的速度增加。此外,上海农业生产部分的氮利用效率处于较低水平,仅为 18.43-27.6%。耕地面积是食物生产和消费系统氮投入的主要驱动因素。这些结果为控制上海食物生产和消费引起的氮污染提供了必要的数据,可为行政部门制定政策提供参考。