Scientia Agricultura Sinica ›› 2026, Vol. 59 ›› Issue (9): 1916-1936.doi: 10.3864/j.issn.0578-1752.2026.09.007

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Spatio-Temporal Evolution and Driving Factors of Carbon Storage in Hilly Areas in Central Sichuan Based on Land Use Change in the Past 40 Years

DENG ChunXiu1(), YAO Li2, WU HongJian1, LI Jie1, SHEN Yue1, LAI Ming1, YU Long1, GUO Wei1, LI JinMeng1, LIN ChaoWen2, LI YuanHong1()   

  1. 1 Institute of Remote Sensing and Digital Agriculture, Sichuan Academy of Agricultural Sciences (Chengdu Agricultural Remote Sensing Sub-center), Chengdu 610066
    2 Agricultural Resources and Environment Institute, Sichuan Academy of Agricultural Sciences, Chengdu 610011
  • Received:2025-06-07 Accepted:2025-08-26 Online:2026-05-01 Published:2026-05-06
  • Contact: LI YuanHong

Abstract:

【Objective】This study aimed to clarify the coupling mechanism between land use change and carbon storage in Suining City, Sichuan Province, is a typical hilly region in the upper reaches of the Yangtze River. Besides, the synergistic pathways for "cropland protection-ecological conservation-carbon sequestration" from 1986 to 2035 were explored. This study could provide a theoretical basis for scientifically and rationally promoting the increase of carbon storage and maintaining the sustainable development of agriculture.【Method】Based on land use data interpreted from remote sensing imagery from 1986 to 2023, the InVEST model was employed to estimate carbon storage across multiple time periods. Geographic detectors and ridge regression were used to analyze spatial differentiation drivers. The PLUS model was used to simulate land use and carbon storage changes under four 2035 scenarios: Natural Development (NDS), Urban Development (UDS), Ecological Priority (EPS), and Cropland Protection (CPS). The changing trends and influencing factors of carbon storage in Suining City over the past 40 years were explored.【Result】(1) Land use transformation patterns. Over the past 40 years, the area of cropland, forest land, and construction land has changed significantly, and land use has undergone a three-stage transition: "cropland contraction-urban expansion-ecological restoration". The proportion of crop land decreased from 66.6% to 46.1%, whereas construction land increased from 6.0% to 13.4%. The dominant transition pathway was cropland-to-forest (56.3%). (2) Bidirectional effects on carbon storage. Regional net carbon storage increased by 28.73×105 t, of which the conversion of cropland to forest land was the most important factor driving the increase of carbon storage, contributing 113.16×105 t to the increase of the core carbon increment, followed by the conversion of cropland to shrub land, which increased carbon storage by 13.13×105 t. In contrast, built-up land expansion resulted in a carbon loss of 14.90×105 t. The carbon storage structure was dominated by soil organic carbon, which accounted for more than 84.0%. (3) Driving mechanisms. Topography-vegetation synergistic effects primarily shaped the spatial heterogeneity of carbon storage. Vegetation indices-including Soil Adjusted Vegetation Index (SAVI), Normalized Difference Vegetation Index (NDVI), and Leaf Area Index (LAI)-accounted for over 62.0% of the explanatory power. Due to limited topographic variability in hilly areas (slope coefficient of variation CV≤0.38), topographic factors exhibited a paradox of "high q-value-low contribution" (actual contribution rate <7.0%). (4) Scenario simulations. The EPS scenario was identified as the optimal carbon-maximum pathway, with a marginal increase in carbon storage (0.2%) achieved by strictly controlling construction land (increase limited to 2.2%) and enhancing coordinated restoration of forest and grassland ecosystems (grassland area increased by 69.9%). In contrast, the CPS scenario induced ecological risks: although cropland expanded by 11.6%, carbon storage declined by 0.1%, and wetland conversion exceeded 50.0%.【Conclusion】Based on an analysis of the impact of land use changes over the past 40 years on carbon storage and its driving factors, optimizing land use structure and implementing a “zonal management” policy represented the key pathway to promoting the steady increase of carbon storage in the hilly region of central Sichuan.

Key words: land use change, carbon storage, InVEST model, PLUS model, Geodetector-Ridge Regression, hilly region of central Sichuan Province

Fig. 1

Distribution of sample points in the study area"

Table 1

Data sources and descriptions of driving factors"

数据类别
Data category
数据名称
Data name
时间
Year
分辨率
Resolution (m)
数据来源
Data source
地形因子
Topographic factor
海拔高度DEM 30 OpenTopography_Copernicus GLO-30 Digital Elevation Model https://opentopography.s3.sdsc.edu/minio/raster/COP30/
坡度SLP 1986, 2009, 2019, 2023 30
山谷深度VD 30
植被指数
Vegetation index
归一化植被指数NDVI 30 中国陆地观测卫星(Landsat)(https://data.cresda.cn)计算分析得出
Calculated and analyzed by China Land Observation Satellite (Landsat) https://data.cresda.cn
叶面积指数LAI 30
增强植被指数EVI 30
土壤调解植被指数SAVI 30
地表水分指数LSWI 30
修正型归一化差异水体指数MNDWI 30
土壤增强指数SER1 30
土壤增强指数SER2 30
土壤增强指数SER3 30
气候因子
Climatic factor
年平均气温TEM 1000 中国1 km分辨率逐月平均气温数据集(1901—2023)
Monthly mean temperature dataset at 1km resolution for China (1901-2023) https://www.tpdc.ac.cn/zh-hans/data/71ab4677-b66c-4fd1-a004-b2a541c4d5bf/
年平均降水PRE 1000 中国1 km分辨率逐月降水量数据集(1901—2023)
Monthly precipitation dataset at 1 km resolution for China (1901 -2023) https://data.tpdc.ac.cn/zh-hans/data/faae7605-a0f2-4d18-b28f-5cee413766a2
社会因子
Social factor
人口数据POP 2000, 2010, 2015, 2020 1000 中国人口空间分布公里网格数据集 https://www.resdc.cn/DOI/DOI.aspx DOIID=32
China Population Spatial Distribution Kilometer Grid Dataset
距道路距离ROAD 1986, 2009, 2019, 2023 30 根据土地利用提取后,数据计算生成
After extraction based on land use, the data is computationally generated

Table 2

Carbon density of different land use types in Suining City (t·hm-2)"

土地利用类型
Land use/Land cover type
地上生物量碳密度
Aboveground biomass carbon density
地下生物量碳密度
Belowground biomass carbon density
土壤有机碳密度(校正)
Soil organic carbon
density
死亡有机质碳密度
Dead organic matter carbon density
耕地Cultivated land 4.02 0.75 91.33 2.11
林地Forest land 22.62 18.03 125.77 2.78
灌木Shrubland 8.67 4.05 84.78 0.87
草地Grassland 3.60 11.70 65.93 7.28
水域Water area 1.59 0.00 67.53 3.98
湿地Wetland 2.10 6.82 56.17 0.21
建设用地 Construction land 0.83 0.08 43.71 0.00
未利用地Unused land 0.59 0.64 28.42 0.96

Table 3

Land use transition matrix settings under different scenarios"

LUCC类型
LUCC type
自然发展情景
Natural development scenario
城市发展情景
Urban development scenario
生态优先情景
Ecological priority scenario
耕地保护情景
Farmland protection scenario
a b c d e f g h a b c d e f g h a b c d e f g h a b c d e f g h
a 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 0 0 0 0 0 0
b 1 1 1 1 1 1 1 1 0 1 0 0 0 0 0 0 1 1 0 1 1 1 0 0 1 1 1 1 1 1 1 1
c 1 1 1 1 1 1 1 1 0 0 1 0 0 0 0 0 0 0 1 0 0 0 0 0 1 0 1 0 0 0 1 0
d 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 0 0 0 1 1 1 0 1 1 1 1 1 1 1 1 1
e 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 0 0 0 1 1 1 0 1 1 1 1 1 1 1 1 1
f 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 0 0 0 0 1 1 1 0 1 1 1 1 1 1 1 1 1
g 1 1 1 1 1 1 1 1 1 0 1 0 0 1 1 0 1 0 1 1 1 1 1 0 1 1 1 1 1 1 1 1
h 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1 1

Table 4

Land use/land cover (LUCC) area changes in Suining City from 1986 to 2023"

LUCC类型
LUCC type
1986-2009 2009-2019 2019-2023 1986-2023
面积
Area (hm2)
变幅
Variation (%)
面积
Area (hm2)
变幅
Variation (%)
面积
Area (hm2)
变幅
Variation (%)
面积
Area (hm2)
变幅
Variation (%)
草地Grassland -3575.30 -71.8 -104.82 -7.5 890.05 68.5 -2790.07 -56.0
耕地Cultivated land -27805.54 -7.9 -79926.70 -24.5 -1274.11 -0.5 -109006.34 -30.8
灌木Shrubland -5627.45 -97.3 26986.71 16949.3 -2026.81 -7.5 19332.46 334.1
建设用地Construction land 29327.39 91.9 5152.97 8.4 4728.70 7.1 39209.06 122.8
林地Forest land 21861.79 22.5 43985.20 37.0 -3479.77 -2.1 62367.22 64.2
湿地Wetlands -719.09 -16.0 -2567.37 -67.9 -337.21 -27.8 -3623.68 -80.5
水域Water area -7439.46 -27.2 6565.33 32.9 1495.62 5.6 621.49 2.3
未利用地Unused land -6022.35 -98.4 -91.32 -93.2 3.53 52.7 -6110.14 -99.8

Fig. 2

Land use maps of Suining City in 1986 (a), 2009 (b), 2019 (c), and 2023 (d)"

Fig. 3

Schematic diagram of the land use transition matrix"

Fig. 4

Spatial distribution of carbon density in Suining City in 1986, 2009, 2019, and 2023"

Table 5

Carbon storage in Suining City from 1986 to 2023"


Year
碳储量
Carbon stock
地上生物量碳
Above-ground biomass carbon
地下生物量碳
Below-ground biomass
carbon
土壤有机碳
Soil organic carbon
死亡有机质碳
Dead organic matter
carbon
含量
Quantity contained
(×105 t)
含量
Quantity contained
(×105 t)
占比
Percentage (%)
含量
Quantity contained
(×105 t)
占比
Percentage (%)
含量
Quantity contained
(×105 t)
占比
Percentage (%)
含量
Quantity contained
(×105 t)
占比
Percentage (%)
1986 561.64 37.74 6.7 21.37 3.8 490.78 87.4 11.75 2.1
2009 567.96 41.03 7.2 24.39 4.3 491.43 86.5 11.11 2.0
2019 595.73 50.19 8.4 32.63 5.5 501.78 84.2 11.13 1.9
2023 590.37 49.27 8.3 32.00 5.4 498.00 84.4 11.11 1.9

Table 6

Changes in carbon storage by land use type in Suining City from 1986 to 2023"

LUCC类型
LUCC type
1986-2009 2009-2019 2019-2023 1986-2023
变化量
Variation
(×105 t)
变幅
Variation
(%)
变化量
Variation
(×105 t)
变幅
Variation
(%)
变化量
Variation
(×105 t)
变幅
Variation
(%)
变化量
Variation
(×105 t)
变幅
Variation
(%)
草地Grassland -3.16 -71.8 -0.09 -7.5 0.79 68.5 -2.47 -56.0
耕地Cultivated land -27.31 -7.9 -78.50 -24.5 -1.25 -0.5 -107.06 -30.8
灌木Shrubland -5.54 -97.3 26.55 16949.3 -1.99 -7.5 19.02 334.1
建设用地Construction land 13.09 91.9 2.30 8.4 2.11 7.1 17.50 122.8
林地Grassland 36.99 22.5 74.42 37.0 -5.89 -2.1 105.53 64.2
湿地Wetland -0.47 -16.0 -1.68 -67.9 -0.22 -27.8 -2.37 -80.5
水域Water area -5.44 -27.2 4.80 32.9 1.09 5.6 0.45 2.3
未利用地Unused land -1.84 -98.4 -0.03 -93.2 0.00 52.7 -1.87 -99.8
合计Total 6.32 1.1 27.78 4.9 -5.36 -0.9 28.73 5.1

Table 7

Matrix of land use changes and carbon storage changes by land use type in Suining City from 1986 to 2023"

面积转移矩阵Area transfer matrix (hm2)
LUCC类型
LUCC type
草地
Grassland
耕地
Cultivated land
灌木
Shrubland
建设用地
Construction land
林地
Forest land
湿地
Wetland
水域
Water area
未利用地
Unused
land
转出
Transfer
out
草地Grassland 539.16 818.32 153.68 268.30 3121.70 7.50 71.25 0.08 4440.84
耕地Cultivated land 1020.77 226682.98 14749.15 37641.09 71907.59 34.72 2326.01 0.40 127679.73
灌木Shrubland 29.51 1398.53 2054.02 229.25 1978.68 0.00 96.67 0.00 3732.65
建设用地Construction land 39.47 4250.35 382.73 24603.99 2088.16 4.79 556.47 0.70 7322.68
林地Forest land 308.89 5028.28 7080.07 4606.49 79179.66 14.82 966.57 1.88 18007.00
湿地Wetland 41.60 1210.99 34.58 728.93 170.48 546.18 1766.84 0.03 3953.46
水域Water area 77.89 2438.18 140.71 1252.80 1038.97 267.95 22176.29 0.55 5217.04
未利用地Unused land 132.64 3528.74 524.19 1804.87 68.65 0.00 54.71 6.57 6113.79
转入Transfer in 1650.77 18673.39 23065.10 46531.74 80374.22 329.78 5838.54 3.65 /
碳储量转移矩阵 Carbon storage transfer matrix(×105 t)
LUCC类型
LUCC type
草地
Grassland
耕地
Cultivated land
灌木
Shrubland
建设用地
Construction land
林地
Forest land
湿地
Wetland
水域
Water area
未利用地
Unused
land
转出
Transfer
out
草地Grassland 0.00 -0.20 0.12 0.10 4.76 -0.02 0.00 -0.04 4.72
耕地Cultivated land 0.18 0.00 13.13 14.90 113.16 -0.77 -0.08 -1.08 139.44
灌木Shrubland -0.11 -13.11 0.00 -0.07 -8.63 -0.02 -0.03 -0.16 -22.13
建设用地Construction land -0.20 -32.79 0.15 0.00 -4.26 -0.47 -0.51 -0.55 -38.63
林地Forest land -2.49 -65.68 5.02 1.12 0.00 -0.10 -0.05 -0.02 -62.20
湿地Wetland 0.03 1.16 0.03 0.32 0.26 0.00 1.10 0.00 2.90
水域Water area 0.01 0.11 0.04 0.31 0.12 -0.98 0.00 -0.02 -0.41
未利用地Unused land 0.12 3.47 0.52 0.81 0.11 0.00 0.04 0.00 5.07
转入Transfer in -2.46 -107.04 19.01 17.49 105.52 -2.36 0.47 -1.87 /

Table 8

Detection results of driving factors for spatial variation of carbon storage in Suining City from 1986 to 2023"

影响因素Influencing factor 驱动因子Driving factor 1986 2009 2019 2023
q β 贡献率Contribution rate (%) q β 贡献率Contribution rate (%) q β 贡献率Contribution rate (%) q β 贡献率Contribution rate (%)
气候因素Climate factors TEM 0.084 9.587 5.7 0.036 1.196 0.1 0.049 14.006 0.5 0.044 6 0.3
PRE 0.052 0.166 0.1 0.005 -0.323 0.0 0.003 -0.880 0.0 0.002 -1.898 0.0
生物因素Biological factors NDVI 0.026 -170.88 30.9 0.115 -53.449 11.9 0.291 -43.115 9.1 0.319 -24.641 7.6
LAI 0.055 51.946 20.0 0.147 45.162 12.9 0.390 46.716 13.2 0.399 28.523 11.0
EVI 0 0.002 0.0 0.064 0.025 0.0 0.120 -2.502 0.2 0.148 0.677 0.1
SAVI 0.035 57.120 14.3 0.070 0.195 0.1 0.143 -423.848 43.9 0.152 -275.299 40.2
地形因素Topographic factors DEM 0.107 0.173 0.1 0.089 0.106 0.0 0.097 0.182 0.0 0.124 0.084 0.0
SLP 0.003 0.024 0.0 0.076 0.682 0.1 0.118 0.454 0.0 0.202 0.517 0.1
VD 0.018 0.028 0.0 0.037 -0.071 0.0 0.075 0.083 0.0 0.096 -0.051 0.0
其他遥感因素Other remote sensing factors LSWI 0.015 -112.032 11.6 0.025 -245.289 11.8 0.128 253.776 23.6 0.147 168.803 23.9
MNDWI 0.02 29.83 4.2 0.030 -141.852 8.3 0.056 -86.220 3.5 0.098 -65.859 6.2
SER1 0.007 37.625 1.8 0.071 -182.486 25.3 0.241 -11.486 2.0 0.218 -16.479 3.5
SER2 0.024 -42.286 7.1 0.040 276.297 21.2 0.037 8.487 0.2 0.075 13.126 0.9
SER3 0.02 -29.83 4.1 0.030 141.852 8.3 0.056 86.220 3.5 0.098 65.859 6.2
社会经济因素Socio-economic factors POP 0.026 -0.001 0.0 0.028 -0.012 0.0 0.026 0.002 0.0 0.025 0.001 0.0
ROAD 0.034 0.002 0.0 0.011 0 0.0 0.018 -0.001 0.0 0.019 -0.001 0.0

Fig. 5

Schematic diagram of ridge regression analysis results for driving factors in 1986(a), 2009(b), 2019(c), and 2023(d)"

Fig. 6

Predicted land use types in 2035 under four scenarios: natural development, urban development, ecological priority, and farmland protection"

Table 9

Predicted land use/land cover types under four development scenarios in 2035"

LUCC类型
LUCC type
2023年基期年
The base year of 2023
2035年自然发展情景
Natural development scenario in 2035
2035年城镇发展情景
Urban development scenarios in 2035
2035年生态优先情景
Ecological priority scenario in 2035
2035年耕地保护情景
Farmland protection scenario in 2035
面积
Area
(hm2)
地类占比
Percentage of land types (%)
面积
Area
(hm2)
地类占比
Percentage of land types (%)
变幅
Amplitude variation (%)
面积
Area
(hm2)
地类占比
Percentage of land types (%)
变幅
Amplitude variation (%)
面积
Area
(hm2)
地类占比
Percentage of land types (%)
变幅
Amplitude variation (%)
面积
Area
(hm2)
地类占比
Percentage of land types (%)
变幅
Amplitude variation (%)
耕地Cultivated land 245356.37 46.1 240743.52 45.2 -1.9 239961.15 45.1 -2.2 237923.33 44.7 -3.0 273812.13 51.4 11.6
建设用地
Construction land
71135.72 13.4 84758.67 15.9 19.1 86100.21 16.2 21.0 72716.49 13.7 2.2 61056.54 11.5 -14.2
水域Water area 28014.83 5.3 29112.03 5.5 3.9 29797.83 5.6 6.4 28642.05 5.4 2.2 25280.28 4.8 -9.8
林地Forest land 159553.89 30.0 149852.79 28.2 -6.1 149553.36 28.1 -6.3 162717.52 30.6 2.0 149867.46 28.2 -6.1
灌木Shrubland 25119.12 4.7 24591.96 4.6 -2.2 23608.62 4.4 -6.1 26079.3 4.9 3.8 20949.39 3.9 -16.7
草地Grassland 2189.93 0.4 2745 0.5 25.7 2478.33 0.5 13.4 3719.61 0.7 69.9 841.23 0.2 -61.5
湿地Wetland 875.96 0.2 456.03 0.1 -48.0 760.41 0.1 -13.2 465.12 0.1 -46.9 456.48 0.1 -47.9
未利用地
Unused land
10.22 0.0 6.57 0.0 -37.6 6.66 0.0 -36.8 3.15 0.0 -69.2 3.06 0.0 -70.9

Table 10

Predicted carbon storage under four development scenarios in 2035"

LUCC类型
LUCC type
2023年基期年
The base year of 2023
2035年自然发展情景
Natural development scenario in 2035
2035年城镇发展情景
Urban development scenarios in 2035
2035年生态优先情景
Ecological priority scenario in 2035
2035年耕地保护情景
Farmland protection scenario in 2035
碳储量
Carbon stock
(×105 t)
碳储量
Carbon stock
(×105 t)
变幅
Amplitude variation (%)
碳储量
Carbon stock
(×105 t)
变幅
Amplitude variation (%)
碳储量
Carbon stock
(×105 t)
变幅
Amplitude variation (%)
碳储量
Carbon stock
(×105 t)
变幅
Amplitude variation (%)
耕地Cultivated land 240.96 236.43 -1.9 235.67 -2.2 233.66 -3.0 268.91 11.6
建设用地Construction land 31.74 37.82 19.2 38.42 21.0 32.45 2.2 27.24 -14.2
水域Water area 20.48 21.28 3.9 21.78 6.4 20.94 2.2 18.48 -9.8
林地Forest land 269.97 253.55 -6.1 253.04 -6.3 275.32 2.0 253.58 -6.1
灌木Shrubland 24.71 24.19 -2.1 23.22 -6.0 25.65 3.8 20.61 -16.6
草地Grassland 1.94 2.43 25.4 2.19 13.2 3.29 69.9 0.74 -61.6
湿地Wetland 0.57 0.30 -47.9 0.50 -13.2 0.30 -46.9 0.30 -47.9
未利用地Unused land 0.003 0.002 -35.7 0.002 -34.8 0.001 -69.2 0.001 -70.1
合计Total 590.37 576.01 -2.4 574.83 -2.6 591.62 0.2 589.86 -0.1

Fig. 7

Schematic map of carbon density distribution in Suining City under natural development, urban development, ecological priority, and farmland protection scenarios in 2035"

Table 11

Distribution of average carbon density per unit under four scenarios (t·hm-2)"

分区
Partition
2023基期年
The base year of
2023
自然发展情景
Natural development scenario
城镇发展情景
Urban development scenario
生态优先情景
Ecological priority scenario
耕地保护情景
Farmland protection scenario
北部低山带
The northern low mountain area
120.98 117.41 117.08 121.19 120.50
涪江冲积带Fujiang alluvial zone 80.75 78.99 78.67 81.80 81.15
琼江丘陵带Qiongjiang hilly belt 111.62 109.16 108.98 111.66 111.66
中心城郊带Central peri-urban belt 69.51 66.58 66.41 70.39 68.68
合计Total 110.92 108.22 108.00 111.15 110.82
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