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Journal of Arid Land  2026, Vol. 18 Issue (11): 1988-2007    DOI: 10.1016/j.jaridl.2026.11.007    
Research article     
Detecting nonlinear threshold effects in water-carbon trade-offs driven by farmland expansion: An Ordered Logit Model approach
ZHAO Minmin, WANG Siyuan*()
Key Laboratory of Water Resources Investigation and Monitoring, Center for Hydrogeology and Environmental Geology Survey, China Geological Survey, Tianjin 300309, China
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Abstract  

Meeting the escalating global food demand while maintaining sustainable ecosystem development poses a pressing global challenge. Since 1990, China's newly reclaimed farmland has been predominantly distributed in arid northwestern regions, where farmland expansion boosts food production but intensifies water consumption and threatens oasis ecological stability. However, conventional continuous models are incapable of identifying nonlinear threshold effects in water-carbon trade-offs, which are essential for targeted ecosystem management. To fill this research gap, this study developed a water-carbon trade-off degree (WCTD) indicator, discretized the WCTD indicator into ordered categorical variables, and adopted the Ordered Logit Model to quantify the impacts of farmland expansion on water-carbon trade-offs of the Heihe River Basin, China. Results showed that in the middle reaches of the Heihe River Basin, farmland expanded by 307.11 km2 from 2001 to 2020, mainly due to conversion from grassland and unused land. The regional annual mean net primary productivity (NPP) and evapotranspiration (ET) both showed significant increasing trends. However, the relatively faster growth rate of ET resulted in a pronounced decrease in water use efficiency (WUE), with a linear trend slope of -0.0072 g C/(mm•m2•a) (P<0.050). The Ordered Logit Model results suggested that increased well density and temperature were both significantly positively associated with the deterioration of the water-carbon trade-off, and that grassland-to-farmland conversion imposed a stronger negative impact than unused land-to-farmland conversion. This is mainly because unused land has extremely low baseline WUE, and its reclamation improves soil and hydrological conditions, thereby greatly enhancing WUE. In comparison, grassland reclamation disrupts ET balance; water consumption increases more rapidly than carbon sequestration, which restricts WUE improvement. This study provides a scientific reference for rational farmland planning in the Heihe River Basin and constructs a discretized modeling analytical framework that can be applied to other arid regions to explore the nonlinear interaction mechanisms of human-driven water-carbon coupled systems.



Key words: arid oasis      farmland expansion      water-carbon trade-off      water use efficiency (WUE)      net primary productivity (NPP)      land use/land cover change (LUCC)      Ordered Logit Model     
Received: 25 March 2026      Published: 30 November 2026
Corresponding Authors: *WANG Siyuan (E-mail: wsylzu007@126.com)
About author: Author contributions

Conceptualization: ZHAO Minmin, WANG Siyuan; Methodology: ZHAO Minmin, WANG Siyuan; Data curation: WANG Siyuan; Formal analysis: ZHAO Minmin, WANG Siyuan; Writing - original draft preparation: ZHAO Minmin; Writing - review and editing: ZHAO Minmin, WANG Siyuan; Funding acquisition: ZHAO Minmin; Supervision: WANG Siyuan. All authors approved the manuscript.

Cite this article:

ZHAO Minmin, WANG Siyuan. Detecting nonlinear threshold effects in water-carbon trade-offs driven by farmland expansion: An Ordered Logit Model approach. Journal of Arid Land, 2026, 18(11): 1988-2007.

URL:

http://jal.xjegi.com/10.1016/j.jaridl.2026.11.007     OR     http://jal.xjegi.com/Y2026/V18/I11/1988

Fig. 1 Distribution of land use/land cover of the middle reaches of the Heihe River Basin in 2020. The farmland expansion patches depict farmland expansion from 2001 to 2020.
Factor Spatial resolution (m) Data source
Net primary productivity (NPP) 500 MOD17A3HGF.061: Terra Net Primary Production Gap-Filled Yearly Global 500m (https://doi.org/10.5067/MODIS/MOD17A3HGF.061)
Evapotranspiration (ET) 500 MOD16A2GF.061: Terra Net Evapotranspiration Gap-Filled 8-Day Global 500m (https://doi.org/10.5067/MODIS/MOD16A2GF.061)
Land use/land cover 30 GLC_FCS30D: global 30-m land-cover dynamic monitoring product (https://data.casearth.cn/thematic/glc_fcs30/314)
Table 1 Data sources and descriptions used for water-carbon trade-off analysis
Fig. 2 Land use/land cover transition matrix in the middle reaches of the Heihe River Basin from 2001 to 2020. Diagonal values are the unchanged areas of each land use type, and off-diagonal values are the areas transferred from the row type to the column type.
Land use/land cover Area (km2)
2001 2020
Farmland 2002.90 2310.01
Woodland 59.40 57.98
Grassland 1887.80 2205.40
Water body 96.42 92.88
Construction land 128.19 170.57
Unused land 7287.91 6625.79
Table 2 Land use/land cover change (LUCC) in the study area from 2001 to 2020
Variable R2 Adjusted R2 Slope Trend P
NPP 0.69 0.68 3.45 g C/(m2•a) Increasing 0.000
ET 0.71 0.70 5.08 mm/a Increasing 0.000
WUE 0.22 0.17 -0.0072 g C/(mm•m2•a) Decreasing 0.039
Table 3 Ordinary least squares (OLS)-derived linear trends of NPP, ET, and water use efficiency (WUE) from 2001 to 2020
Fig. 3 Temporal dynamics of regional average evapotranspiration (ET) and net primary productivity (NPP) in the middle reaches of the Heihe River Basin from 2001 to 2020
Fig. 4 Spatiotemporal changes in NPP in the middle reaches of the Heihe River Basin from 2001 to 2020. (a), Theil-Sen slope; (b), Mann-Kendall (MK) significance test; (c), change trend of NPP.
Fig. 5 Spatiotemporal changes in ET in the middle reaches of the Heihe River Basin from 2001 to 2020. (a), Theil-Sen slope; (b), MK significance test; (c), change trend of ET.
Fig. 6 Temporal dynamics of regional average water use efficiency (WUE) in the middle reaches of the Heihe River Basin from 2001 to 2020
Fig. 7 Spatiotemporal changes in WUE in the middle reaches of the Heihe River Basin from 2001 to 2020. (a), Theil-Sen slope; (b), MK significance test; (c), change trend of WUE.
Fig. 8 Impact of farmland expansion on NPP, ET, and WUE in the middle reaches of the Heihe River Basin from 2001 to 2020
Factor β OR P 95.00% confidence interval for OR
Lower bound Upper bound
WCTD1≤ -0.30 g C/(mm•m2) -4.73 0.01 0.000 0.00 0.09
-0.30 g C/(mm•m2)<WCTD1≤0.00 g C/(mm•m2) -2.74 0.06 0.017 0.01 0.61
Temperature -0.29 0.75 0.030 0.58 0.97
Well density -0.51 0.60 0.001 0.45 0.82
Grassland-to-farmland -0.77 0.46 0.012 0.25 0.85
Unused land-to-farmland 0.00 1.00 - - -
Table 4 The Ordered Logit Model regression analysis of the influencing factors of water-carbon trade-off degree 1 (WCTD1)
Factor >0.30 km2
(N=246)
>0.38 km2
(N=223)
>0.40 km2 (N=144)
β P β P β P
Temperature -0.29 0.030 -0.33 0.017 -0.37 0.039
Well density -0.51 0.001 -0.44 0.006 -0.49 0.012
Grassland-to-farmland -0.77 0.012 -0.78 0.016 -0.33 0.381
Unused land-to-farmland 0.00 - 0.00 - 0.00 -
Model fit (likelihood ratio χ2) 37.51 0.000 34.66 0.000 24.07 0.000
Table 5 Sensitivity analysis of the Ordered Logit Model under different patch size thresholds
Factor Jenks Natural Breaks
(-0.30 g C/(mm•m2))
25.00% quantile
(-0.35 g C/(mm•m2))
33.00% quantile
(-0.28 g C/(mm•m2))
β P β P β P
Temperature -0.29 0.030 -0.29 0.031 -0.30 0.026
Well density -0.51 0.001 -0.53 0.001 -0.49 0.002
Grassland-to-farmland -0.77 0.012 -0.83 0.008 -0.78 0.011
Unused land-to-farmland 0.00 - 0.00 - 0.00 -
Model fit (likelihood ratio χ2) 37.51 0.000 40.04 0.000 37.40 0.000
Table 6 Sensitivity analysis of the Ordered Logit Model under different WCTD1 classification thresholds
Factor β OR P 95.00% confidence interval for OR
Lower bound Upper bound
WCTD2≤0.50 -5.35 0.00 0.000 0.00 0.05
0.50<WCTD2≤1.00 -2.79 0.06 0.016 0.01 0.60
Temperature -0.26 0.77 0.049 0.59 1.00
Well density -0.65 0.52 0.000 0.38 0.71
Grassland-to-farmland -0.92 0.40 0.004 0.21 0.74
Unused land-to-farmland 0.00 1.00 - - -
Table 7 The Ordered Logit Model regression analysis of the influencing factors of water-carbon trade-off degree 2 (WCTD2)
Variable Unstandardized coefficient Standardized coefficient t P Collinearity statistics
β Standard error β Tolerance VIF
Constant 0.12 0.13 - 0.89 0.373 - -
Temperature -0.02 0.02 -0.11 -1.57 0.118 0.77 1.29
Well density -0.07 0.02 -0.25 -3.73 0.000 0.75 1.33
Land conversion type 0.14 0.04 0.22 3.66 0.000 0.96 1.04
Table 8 Linear regression results for the influencing factors of WCTD1
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