Identification of anthropogenic parameters for a regional nitrogen balance model via field investigation of six ecosystems in China

• Published in: Biogeochemistry Vol. 94; no. 2; pp. 175 - 190
• Main Authors: Liu, Chen, Wang, Qinxue, Lei, Alin, Yang, Yonghui, Ouyang, Zhu, Lin, Yaoming, Li, Yan, Wang, Kelin
• Format: Journal Article
• Language: English
• Published: Dordrecht Dordrecht : Springer Netherlands 01.06.2009; Springer; Springer Netherlands; Springer Nature B.V
• Subjects: Agricultural land; Agricultural practices; Agrochemicals; Agroecosystems; Animal wastes; Anthropogenic factors; Biogeosciences; Crops; Earth and Environmental Science; Earth Sciences; Economic conditions; Ecosystems; Environmental Chemistry; Farming systems; Feces; Fertilizers; Food consumption; Food groups; Food intake; Geochemistry; Human influences; Irrigation systems; Life Sciences; Livestock; Livestock feeds; Nitrogen; Nitrogen balance; Organic farming; Rivers; Rural areas; Socioeconomics; Soils; Urban areas; Urea; Waste byproducts; Waste disposal; China, People's Rep; Field investigation; Nitrogen flow; Food intake; Ecosystem; Farming method
• ISSN: 0168-2563; 1573-515X
• DOI: 10.1007/s10533-009-9317-9

To evaluate the impact of human behavior (with regard food consumption, waste disposal and farming method) on nitrogen flow, a field investigation was conducted in six typical ecosystems in China. A number of parameters for regional nitrogen balance models were identified during the investigation. The results show that the average per-capita daily protein intake is 107 g. While there is an insignificant difference in total protein intake among the different ecosystems, protein intake from all food groups, except for eggs, is significantly different (P <= 0.05). Differences in diet, along with those in socio-economic conditions, reflect differences in the characteristics of the ecosystems. Regarding per-capita annual potential nitrogen loading from human excrement, a considerable difference exists between the urban rich and the rural poor. In urban areas, approximately 1.02 kg N is returned to farmlands and 5.49 kg N is directly discharged into rivers. In rural regions, on the other hand, approximately 4.33 kg N is returned to farmlands and 1.60 kg N is directly discharged into rivers. Furthermore, urea and mixed fertilizers constitute the most common chemical fertilizers in the study area. Fertilizer diversification is practiced in a range of agricultural lands, paddy-fields and irrigated plains. In the oasis and paddy-field agricultural systems, many of the agricultural by-products (e.g., straw) are burned or mixed with base-fertilizers and plowed into the soil. In irrigated agricultural systems, over 70% of agricultural by-products are recycled as livestock feed. In most instances, livestock excrement is directly reduced in the pasturelands or reused in the fields as manure. Occasionally, as in the case of large-scale breeding, excrements are usually abandoned.