YANG Yanan, ZHANG Xiaohui, CHEN Hong, JIAO Yongjie, DENG Xiaowen, YUAN Xuezhu, DONG Jing, YANG Jing. Nitrogen use efficiency in stereoscopic planting rice field in North ChinaJ. Chinese Journal of Eco-Agriculture, 2015, 23(7): 812-822. DOI: 10.13930/j.cnki.cjea.150125
Citation: YANG Yanan, ZHANG Xiaohui, CHEN Hong, JIAO Yongjie, DENG Xiaowen, YUAN Xuezhu, DONG Jing, YANG Jing. Nitrogen use efficiency in stereoscopic planting rice field in North ChinaJ. Chinese Journal of Eco-Agriculture, 2015, 23(7): 812-822. DOI: 10.13930/j.cnki.cjea.150125

Nitrogen use efficiency in stereoscopic planting rice field in North China

  • To control serious agricultural non-point source pollution and improve use efficiency of nitrogen (N) fertilizer in North China, this study investigated nitrogen use efficiency in different planting patterns of paddy fields in a typical rice cultivation zone in Baodi of Tianjin City. With an entire paddy field ecosystem as the basic research unit, N migration and transformation model in paddy field was established based on N input and output. In order to explore N uptake and use efficiency in coTo control serious agricultural non-point source pollution and improve use efficiency of nitrogen (N) fertilizer in North China, this study investigated nitrogen use efficiency in different planting patterns of paddy fields in a typical rice cultivation zone in Baodi of Tianjin City. With an entire paddy field ecosystem as the basic research unit, N migration and transformation model in paddy field was established based on N input and output. In order to explore N uptake and use efficiency in conventional rice field pattern (CK: rice monoculture) and stereoscopic planting rice field pattern (RF: rice-fish-shrimp-crab co-culture + bund + ditch), a field experiment was conducted to analyze the characteristics of N input and N output. The differences in N use efficiency and yield of rice between two paddy planting patterns were investigated too. Results showed that N input of two rice field patterns was mainly from irrigation, fertilization and precipitation. N input from fertilizer in RF system was 128.25 kg(N)·hm-2, 11.75 kg(N)·hm-2 less than that of CK, and was 14%52% less than that of other rice planting regions in South China. In RF system, N input at source was limited, thus reducing the risk of nutrient loss. N output of CK system was composed of soil fixation, ammonia volatilization, N loss via lateral seepage, and crop N uptake. In addition to components of N output of CK, N output of RF system contained N absorptions by fishes, shrimps and crabs. Due to special bund-ditch ecological purification in RF system, N loss through lateral seepage dropped by 9.33 kg(N)·hm-2 and NO3-N was the main form of lateral seepage. N loss via ammonia volatilization in RF and CK systems was 8.91 kg·hm-2 and 21.54 kg·hm-2, respectively. Ammonia volatilization rate in RF system accounted for 6.9% of total amount of applied fertilizer, which was 8.5% less than that in CK and 10.3% less than the national average. Compared with CK, RF system harvested 6.65% higher rice yield. N uptake by rice and aquatic materials was 271.72 kg(N)·hm-2 in RF system, 255.05 kg(N)·hm-2 in CK system. The results suggested that breeding fishes, shrimps and crabs did not reduced rice yield. N use efficiency in RF system reached 64.3%, which was 19.7% higher than that in CK. RF not only achieved high rice yield, but also reduced N loss in paddy fields. Therefore stereoscopic planting rice field was feasible in North China where irrigation demands were well met. This study provided a critical reference for controlling agricultural non-point source pollution in North China.
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