Abstract:
China ranks first globally in terms of vegetable cultivation area and production. Vegetable fields have become significant sources of nitrous oxide (N
2O) emissions owing to high fertilizer and irrigation inputs. By integrating field observational data from 2000 to 2023, this study assessed the characteristics and factors influencing N
2O emissions during the Chinese vegetable system growing season. Results exhibited that the average N
2O emissions from vegetable fields was 7.32 kg(N)·hm
‒2. Emissions were higher in northern China 8.13 kg(N)·hm
‒2 than in southern China 6.8 kg(N)·hm
‒2, with an increase of 19.4%. Greenhouse vegetable systems 7.93 kg(N)·hm
‒2 emitted 44.4% additional N
2O than open-field systems 5.49 kg(N)·hm
‒2. Among crop types, fruit vegetables 8.43 kg(N)·hm
‒2 had significantly higher emissions than leafy 5.28 kg(N)·hm
‒2 and root/tuber vegetables 3.61 kg(N)·hm
‒2, by 59.7% and 133.5%, respectively. The average N
2O emission factor was 1.48%. Southern China (1.78%) exhibited a 64.8% higher emission factor than northern China (1.08%), and open-field systems (1.82%) were 30.9% higher than greenhouse systems (1.39%). Fruit vegetables (1.45%) also exhibited higher emission factors than leafy (1.35%) and root/tuber vegetables (0.90%) by 7.4% and 61.1%, respectively. The yield-scaled N
2O emissions averaged 0.125 kg·t
‒1. This value was higher in the southern (0.145 kg·t
‒1) than in the northern regions (0.103 kg·t
‒1), and in open-field (0.151 kg·t
‒1) than in greenhouse systems (0.118 kg·t
‒1), with increases of 40.8% and 28.0%, respectively. Fruit vegetables (0.138 kg·t
‒1) had higher yield-scaled emissions than leafy (0.122 kg·t
‒1) and root/tuber vegetables (0.036 kg·t
‒1), by 13.1% and 273.0%, respectively. At the national scale, N
2O and yield-scaled emissions were significantly and positively correlated with nitrogen application rates, whereas no significant effect was observed on emission factors. The combined application of organic and inorganic fertilizers significantly increased N
2O emissions compared to the sole application of either fertilizer, although it had no significant impact on the emission factor. Both acidic and alkaline soil conditions significantly increased N
2O emissions, and acidity increased the emission factor. Over-irrigation led to increased N
2O emissions, emission factors, and yield-scale emissions. In conclusion, a comprehensive understanding of regional, agronomic, and crop type differences in N
2O emissions and emissions parameters is essential for accurately assessing and mitigating N
2O emissions from vegetable systems in China. Nationwide strategies, such as optimized nitrogen fertilization, water-saving irrigation, and acidic soil amelioration, are recommended to mitigate N
2O emissions during intensive vegetable production.