邓维忠, 许中坚. 湖南省农业碳排放特征及碳达峰分析[J]. 中国生态农业学报 (中英文), 2024, 32(2): 206−217. DOI: 10.12357/cjea.20230423
引用本文: 邓维忠, 许中坚. 湖南省农业碳排放特征及碳达峰分析[J]. 中国生态农业学报 (中英文), 2024, 32(2): 206−217. DOI: 10.12357/cjea.20230423
DENG W Z, XU Z J. Characteristics of agricultural carbon emissions and carbon peak analysis in Hunan Province[J]. Chinese Journal of Eco-Agriculture, 2024, 32(2): 206−217. DOI: 10.12357/cjea.20230423
Citation: DENG W Z, XU Z J. Characteristics of agricultural carbon emissions and carbon peak analysis in Hunan Province[J]. Chinese Journal of Eco-Agriculture, 2024, 32(2): 206−217. DOI: 10.12357/cjea.20230423

湖南省农业碳排放特征及碳达峰分析

Characteristics of agricultural carbon emissions and carbon peak analysis in Hunan Province

  • 摘要: 了解湖南省农业碳排放特征及影响因素, 可为湖南省绿色低碳农业发展提供科学依据。基于统计年鉴对作物种植面积、农业物资投入量及畜禽养殖量进行数据整合, 利用联合国政府间气候变化专门委员会经典碳排放计算理论计算湖南省2007—2020年间农业碳排放量。以2007年为基期年, 采用Kaya碳排式和对数均值迪氏分解法(Logarithmic Mean Divisia Index, 以下简称LMDI)分析其影响因素, 并引入灰色预测模型gray forecasting model, 以下简称GM (1, 1)预测湖南省2021—2040年间碳排放量。计算结果表明, 湖南省农业碳排放量呈现出三段式变化: 因2008年特大冰雪灾害对农业产生严重影响, 农业碳排放量在2007—2008年间呈下降趋势; 2009—2015年稳步上升并于2015年达到峰值(6550万t); 2015—2020年间整体呈现下降趋势。与此同时, 不同地市间存在明显差异: 长沙、湘潭、衡阳、邵阳、岳阳、常德、益阳于2015年前后达峰, 而其他地市, 如株洲、张家界、郴州、永州、怀化、湘西在2018年前均有一段平稳上升期, 娄底波动上升, 因此难以在2030年前实现碳达峰。湖南省各地市农业碳排放强度呈下降趋势, 2007年农业碳排放强度越大的地市其在后续年份中农业碳排放强度下降幅度越大。2007—2020年间各地市农业碳排放量平均变异系数为42%, 农业碳排放强度平均变异系数为20%, 说明地市之间的农业碳排放量差异程度远大于农业碳排放强度差异程度。农业碳排放源排放占比从大到小依次为: 农田土地利用>畜禽养殖>农资投入。地区经济发展水平、劳动力水平和农村总用电量对增加农业碳排放量起主要作用, 其中地区经济发展水平、农村总用电量是主要影响因素; 农业生产效率、农业产业结构、地区产业结构、农村居民人均用电量的倒数在农业碳排放量减少的过程中起重要作用。本文提出优化产业结构、各地因地制宜地推动绿色创新、加强政府职能等建议, 以期为湖南省农业碳减排决策提供参考。

     

    Abstract: Understanding the characteristics of and factors influencing agricultural carbon emissions in Hunan Province can provide a scientific basis for the development of green and low-carbon agriculture in Hunan Province. By reviewing the Hunan Statistical Yearbook and the statistical yearbooks of various cities and regions, we integrated the data on crop area, agricultural inputs, and livestock and poultry production, and calculated the agricultural carbon emissions of Hunan Province from 2007 to 2020 using the classical carbon emission calculation theory of the Intergovernmental Panel on Climate Change (IPCC). Taking 2007 as the base year, the Kaya carbon emission formula and Logarithmic Mean Divisia Index (LMDI) were used to analyze the influencing factors, whereas the grey prediction model GM (1, 1) was introduced to predict the carbon emissions of Hunan Province during the period of 2021–2040. The calculation results showed that the carbon emissions in Hunan Province were 6.15 × 107 t in 2020, and the carbon emission intensity was 1.01 t·(×104¥)−1, with the peak reached in 2015. Agricultural carbon emissions in Hunan Province showed a three-stage change. Due to the severe impact of the 2008 snow and ice disaster on agriculture, agricultural carbon emissions showed a decreasing trend during 2007–2008, a steady increase during 2009–2015, a peak in 2015, and an overall decreasing trend during 2015–2020. At the same time, there were obvious differences among different cities: Changsha, Xiangtan, Hengyang, Shaoyang, Yueyang, Changde, and Yiyang reached their peak carbon emissions around 2015, whereas the other cities failed to reach their peaks before 2030. Agricultural carbon emission intensity in all cities and towns in Hunan Province showed decreasing trend; the larger the agricultural carbon emission intensity in the base year, the larger the decrease in agricultural carbon emission intensity in the following years. The average coefficient of variation of agricultural carbon emissions in each city between 2007 and 2020 was 42%, whereas the average coefficient of variation of agricultural carbon intensity was 20%. This indicates that the difference in agricultural carbon emissions between cities was much larger than the difference in agricultural carbon intensity. The proportion of agricultural carbon emission sources followed the order of farmland utilization > livestock and poultry production > agricultural inputs. The level of regional economic development, labor force level, and total rural electricity consumption play major roles in increasing agricultural carbon emissions; the level of regional economic development and total rural electricity consumption are the main influencing factors, and agricultural production efficiency, agricultural industrial structure, regional industrial structure, and the reciprocal of the per capita electricity consumption of rural residents play important roles in the process of decreasing agricultural carbon emissions. The study shows that agricultural carbon emissions in Hunan Province peaked in 2015. In order to achieve the goal of carbon neutrality and provide reference for the decision-making of agricultural carbon emission reduction in Hunan Province, this paper puts forward suggestions such as optimizing the industrial structure, promoting green innovation according to local conditions, and strengthening government functions.

     

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