Rice is an important part of the food system in China and the world. It is of great significance to study the life cycle carbon footprint of rice food system from the perspective of food system for low-carbon transformation and green development. Based on statistics from 22 major rice-producing provinces in China in 2018, the cradle-to-market carbon footprint of Rice food systems in China, including its structural composition, regional differences and rice type differences was calculated and analyzed by using the life cycle assessment (LCA) method and the CF-Rice rice carbon footprint calculation tool developed by the International Rice Research Institute (IRRI). The results showed that 1) when comparing carbon footprint per unit production (CO2 eq), the carbon footprint was in the order of late indica rice (2.31 kg?kg-1), middle indica rice (1.32 kg?kg-1), japonica rice (1.13 kg?kg-1) and early indica rice (1.08 kg?kg-1). When comparing carbon footprint per unit area (CO2 eq), the carbon footprint was in the order of late indica rice (9.15×103 kg?hm-2), middle indica rice (6.34×103 kg?hm-2), japonica rice (5.56×103 kg?hm-2) and early indica rice (4.16×103 kg?hm-2); 2) Methane (CH4) in paddy field was the most important component of the carbon footprint of rice food system, accounting for 36.2%-71.5%, followed by fertilization (8.69%-20.0%), harvest (8.41%-18.5%) and prenatal (4.97%-12.1%). Mechanical operations, storage, processing, packaging and transportation, although only accounting for less than 10%, were also significant sources of emissions; 3) early indica rice, middle indica rice and late indica rice showed no obvious spatial distribution pattern, while the main producing areas of japonica rice had a large spatial span and showed an increasing trend of carbon footprint from north to south, specifically as follows: except for Shandong, the carbon footprint of japonica rice in Northeast (Heilongjiang, Jilin, Liaoning) and North China (Inner Mongolia, Hebei) was lower than that in East (Anhui, Jiangsu, Zhejiang), central (Henan, Hubei) and southwestern China (Yunnan); 4) from the perspective of the composition of greenhouse gases, the contribution rate of CH4 to the carbon footprint of rice food system was the highest, reaching 20.1%-76.4%, followed by that of CO2 (21.1%-72.3%), and that of N2O (1.76%-10.7%) was the lowest. The regional and type differences of rice food system carbon footprint were mainly related to climatic conditions, planting management measures and emission factors. Hence, in order to reduce the carbon emissions of rice food system, it is necessary to take overall consideration to reduce the CH4 emission of rice field, improve water and fertilizer management, reduce energy consumption, and decrease food loss and waste.