Regional Sustainability ›› 2025, Vol. 6 ›› Issue (3): 100229.doi: 10.1016/j.regsus.2025.100229cstr: 32279.14.REGSUS.2025019
• Research article • Previous Articles Next Articles
Mohammad Reza PAKRAVAN-CHARVADEHa,*(
), Jeyran CHAMCHAMa, Rahim MALEKNIAb
Received:2024-10-21
Accepted:2025-05-29
Published:2025-06-30
Online:2025-07-08
Contact:
Mohammad Reza PAKRAVAN-CHARVADEH
E-mail:pakravan.m@lu.ac.ir
Mohammad Reza PAKRAVAN-CHARVADEH, Jeyran CHAMCHAM, Rahim MALEKNIA. How climate change adaptation strategies and climate migration interact to control food insecurity?[J]. Regional Sustainability, 2025, 6(3): 100229.
Table 1
Descriptive results of the Household Food Insecurity Access Scale (HFIAS)."
| Category | Question | Never (%) | Rarely (%) | Sometime (%) | Often (%) |
|---|---|---|---|---|---|
| Worrying about food availability | Q1: worrying about food availability | 38.21 | 30.11 | 17.19 | 14.49 |
| Preferred food | Q2: unable to eat preferred food | 41.62 | 29.41 | 21.57 | 7.40 |
| Limited variety of food | Q3: eating a limited variety of food | 43.21 | 26.02 | 20.28 | 10.49 |
| Unwanted food | Q4: eating foods that you have to eat unappealing food | 42.93 | 26.01 | 24.00 | 7.06 |
| Smaller meals | Q5: eating a smaller meal | 45.93 | 27.02 | 19.87 | 7.18 |
| Fewer meals | Q6: eating fewer meals in a day | 57.48 | 20.88 | 16.92 | 4.72 |
| Food shortage | Q7: no food to eat at home | 65.21 | 18.58 | 11.51 | 4.70 |
| Hunger at bedtime | Q8: going to bed hungry at night | 70.33 | 16.51 | 9.06 | 4.10 |
| Whole-day without any food | Q9: not eating for a whole day and night | 68.57 | 15.18 | 10.13 | 6.12 |
Table 2
Descriptive statistics of climate migration, food insecurity, and climate change adaptation strategies."
| Factor | Item | Factor loading | Descriptive statistic | VIF | |||||||
|---|---|---|---|---|---|---|---|---|---|---|---|
| Original sample | Sample mean | SD | t-statistics | P-value | Mean | Average | CV | ||||
| Climate migration | I am willing to move to another region | 0.867 | 0.868 | 0.027 | 32.148 | 0.001 | 1.661 | 1.738 | 0.016 | 2.282 | |
| I feel prepared to migrate if necessary | 0.872 | 0.868 | 0.031 | 28.000 | 0.001 | 1.731 | 0.018 | 2.254 | |||
| I would be willing to leave my community | 0.937 | 0.937 | 0.009 | 104.111 | 0.001 | 1.823 | 0.005 | 3.326 | |||
| Food insecurity | Worrying about food availability | 0.588 | 0.590 | 0.087 | 6.782 | 0.001 | 1.194 | 0.804 | 0.073 | 1.337 | |
| Preferred food | 0.832 | 0.825 | 0.027 | 30.556 | 0.001 | 0.961 | 0.023 | 2.371 | |||
| Limited variety of food | 0.811 | 0.807 | 0.030 | 26.900 | 0.001 | 0.990 | 0.030 | 2.650 | |||
| Unwanted food | 0.846 | 0.841 | 0.028 | 30.036 | 0.001 | 0.951 | 0.029 | 3.504 | |||
| Smaller meals | 0.830 | 0.826 | 0.026 | 31.769 | 0.001 | 0.884 | 0.029 | 3.321 | |||
| Fewer meals | 0.764 | 0.764 | 0.033 | 23.152 | 0.001 | 0.693 | 0.048 | 2.215 | |||
| Food shortage | 0.701 | 0.704 | 0.052 | 13.538 | 0.001 | 0.561 | 0.093 | 2.387 | |||
| Going to bed hungry | 0.643 | 0.645 | 0.061 | 10.574 | 0.001 | 0.470 | 0.130 | 2.645 | |||
| Full day without eating | 0.462 | 0.465 | 0.078 | 5.962 | 0.001 | 0.540 | 0.144 | 1.724 | |||
| Climate change adaptation strategies | Economic strategies | Non-agricultural activity outside the farm | 0.946 | 0.929 | 0.133 | 6.985 | 0.001 | 1.772 | 1.763 | 0.075 | 3.586 |
| Non-agricultural employment (labor, sales, etc.) | 0.916 | 0.902 | 0.118 | 7.644 | 0.001 | 1.852 | 0.064 | 3.771 | |||
| Getting a loan | 0.915 | 0.899 | 0.123 | 7.309 | 0.001 | 1.871 | 0.066 | 3.323 | |||
| Using personal savings | 0.917 | 0.902 | 0.119 | 7.580 | 0.001 | 1.724 | 0.069 | 3.130 | |||
| Reducing household expenses | 0.944 | 0.924 | 0.143 | 6.462 | 0.001 | 1.671 | 0.086 | 3.681 | |||
| Livestock sale | 0.850 | 0.831 | 0.127 | 6.543 | 0.001 | 1.692 | 0.075 | 2.823 | |||
| Irrigation management strategies | Changing the irrigation system | 0.814 | 0.812 | 0.030 | 27.067 | 0.001 | 1.750 | 1.705 | 0.017 | 1.742 | |
| Improving the coverage of water transmission channels | 0.787 | 0.781 | 0.034 | 22.971 | 0.001 | 1.700 | 0.020 | 1.692 | |||
| Use of alternative water sources (rainwater, sewage, etc.) | 0.538 | 0.532 | 0.076 | 7.000 | 0.001 | 1.651 | 0.046 | 1.200 | |||
| Management of irrigation intervals | 0.712 | 0.712 | 0.052 | 13.692 | 0.001 | 1.832 | 0.028 | 1.414 | |||
| Watershed management activities (dam, gabion, trust, etc.) | 0.513 | 0.512 | 0.074 | 6.919 | 0.001 | 1.594 | 0.046 | 1.151 | |||
| Organic-oriented strategies | Weed management | 0.745 | 0.740 | 0.047 | 15.745 | 0.001 | 2.131 | 1.778 | 0.022 | 1.565 | |
| Use of organic fertilizer | 0.774 | 0.772 | 0.036 | 21.444 | 0.001 | 1.630 | 0.022 | 1.556 | |||
| Organic farming | 0.794 | 0.794 | 0.026 | 30.538 | 0.001 | 1.640 | 0.016 | 1.632 | |||
| Diversifying crops | 0.864 | 0.863 | 0.024 | 35.958 | 0.001 | 1.711 | 0.014 | 2.283 | |||
| Sustainable development -oriented strategies | Changing the crop cultivation deadline | 0.719 | 0.716 | 0.046 | 15.565 | 0.001 | 1.583 | 1.597 | 0.029 | 1.592 | |
| Conservation tillage | 0.729 | 0.724 | 0.044 | 16.455 | 0.001 | 1.684 | 0.026 | 1.780 | |||
| Agricultural land leveling | 0.739 | 0.734 | 0.047 | 15.617 | 0.001 | 1.910 | 0.025 | 1.777 | |||
| Changing the time of crop harvest | 0.546 | 0.540 | 0.063 | 8.571 | 0.001 | 1.590 | 0.040 | 1.301 | |||
| Multi-cropping | 0.813 | 0.811 | 0.025 | 32.440 | 0.001 | 1.570 | 0.016 | 2.012 | |||
| Compliance with crop rotation | 0.747 | 0.743 | 0.042 | 17.690 | 0.001 | 1.114 | 0.038 | 1.701 | |||
| Reducing the distance between crop rows | 0.656 | 0.653 | 0.052 | 12.558 | 0.001 | 1.732 | 0.030 | 1.604 | |||
| Crop variety management strategies | High-yielding varieties | 0.682 | 0.686 | 0.045 | 15.244 | 0.001 | 1.651 | 1.624 | 0.027 | 1.235 | |
| Using cold-resistant and pest-resistant varieties | 0.809 | 0.806 | 0.033 | 24.424 | 0.001 | 1.692 | 0.020 | 1.757 | |||
| Using varieties resistant to drought | 0.778 | 0.772 | 0.040 | 19.300 | 0.001 | 1.612 | 0.025 | 1.702 | |||
| Using varieties resistant to salt | 0.819 | 0.816 | 0.026 | 31.385 | 0.001 | 1.544 | 0.017 | 1.721 | |||
Table 4
Reliability and validity of climate migration, food insecurity, and climate change adaptation strategies."
| Factor | Cronbach’s Alpha | Dillon-Goldstein’s Rho | CR | AVE | |
|---|---|---|---|---|---|
| Climate migration | 0.872 | 0.880 | 0.922 | 0.797 | |
| Food insecurity | 0.882 | 0.940 | 0.904 | 0.522 | |
| Climate change adaptation strategies | Economic strategies | 0.961 | 1.002 | 0.969 | 0.837 |
| Irrigation management strategies | 0.706 | 0.742 | 0.810 | 0.568 | |
| Organic-oriented strategies | 0.805 | 0.807 | 0.873 | 0.633 | |
| Sustainable development-oriented strategies | 0.834 | 0.846 | 0.876 | 0.506 | |
| Crop variety management strategies | 0.775 | 0.779 | 0.856 | 0.599 | |
Table 5
Results of the Structural Equation Modeling (SEM)."
| Factor | Effect pathway | Original sample | Sample mean | SD | t-statistic | P-value | |
|---|---|---|---|---|---|---|---|
| Economic strategies | Climate migration | Direct effect | -0.046 | -0.048 | 0.009 | 4.721 | 0.000 |
| Indirect effect | -0.008 | -0.008 | 0.001 | 4.709 | 0.000 | ||
| Total effect | -0.054 | -0.040 | 0.008 | 4.580 | 0.000 | ||
| Food insecurity | Direct effect | -0.060 | -0.064 | 0.012 | 4.818 | 0.000 | |
| Irrigation management strategies | Climate migration | Direct effect | -0.201 | -0.209 | 0.079 | 2.542 | 0.011 |
| Indirect effect | -0.026 | -0.027 | 0.007 | 3.515 | 0.000 | ||
| Total effect | -0.227 | -0.236 | 0.082 | 2.770 | 0.006 | ||
| Food insecurity | Direct effect | -0.192 | -0.200 | 0.084 | 2.277 | 0.023 | |
| Organic-oriented strategies | Climate migration | Direct effect | -0.051 | -0.045 | 0.013 | 3.790 | 0.000 |
| Indirect effect | -0.024 | -0.024 | 0.006 | 3.559 | 0.000 | ||
| Total effect | -0.075 | -0.073 | 0.022 | 3.225 | 0.000 | ||
| Food insecurity | Direct effect | -0.177 | -0.179 | 0.049 | 3.554 | 0.000 | |
| Sustainable development-oriented strategies | Climate migration | Direct effect | -0.061 | -0.069 | 0.015 | 3.946 | 0.000 |
| Indirect effect | -0.004 | -0.004 | 0.012 | 0.345 | 0.731 | ||
| Total effect | -0.057 | 0.064 | 0.066 | 0.862 | 0.389 | ||
| Food insecurity | Direct effect | -0.031 | -0.032 | 0.009 | 3.396 | 0.000 | |
| Varity management strategies | Climate migration | Direct effect | -0.287 | -0.276 | 0.068 | 4.241 | 0.000 |
| Indirect effect | -0.008 | -0.009 | 0.012 | 0.668 | 0.505 | ||
| Total effect | -0.295 | 0.267 | 0.070 | 3.948 | 0.000 | ||
| Food insecurity | Direct effect | -0.062 | -0.064 | 0.085 | 0.725 | 0.469 | |
| Food insecurity | Climate migration | Direct effect | 0.134 | 0.131 | 0.059 | 2.282 | 0.023 |
Table S1
The description of all statistics for assessing the reliability and validity of the Structural Equation Modeling (SEM)."
| Statistic | Description | Equation | Explanation |
|---|---|---|---|
| λ | It describes the correlation between an observed variable and underlying latent variable. | λ is the factor loading (Pearson correlation coefficient); Cov(X, Y) is the covariance between observed variable (X) and latent variable (Y); Var(X) is the variance of X; and Var(Y) is the variance of Y. The range of λ is between -1.000 and 1.000. λ value above 0.500 is considered acceptable relationship; λ value ranging from 0.400 to 0.500 is generally considered to reflect moderate relationship; while λ value below 0.400 may indicate weak relationship. | |
| SRMR | It is calculated by the square root of the difference between the observed and predicted covariance matrices. | SRMR is the Standardized Root Mean Square Residual; i is the observation value; n is the total number of observations; Oii is the observed covariance matrix; and Pii is the predicted covariance matrix. The range of SRMR is between 0.000 and 1.000, and SRMR value less than 0.080 is generally considered a good fitting. | |
| dULS | It is the sum of squared differences between the observed and predicted covariance matrices. | dULS is the Squared Euclidean distance; m is the total number of variables; Oij is the observed matrix for the observation ith and variable jth; and Pij is the predicted matrix for the observation ith and variable jth. There is no fixed range for dULS, but lower value indicates a better fitting. | |
| dG | It is similar to dULS, but it takes into account the degrees of freedom. | dG is the Geodesic Distance; and δ2 ij is the variance associated with the observed matrix Oij. Like dULS, lower values indicate a better fitting, with no specific upper limit. | |
| χ² | It is a statistical test used to determine if there is a significant association between categorical variables. | χ² is the Chi-Square; L is the total number of categories; Ol is the observed frequency (count) for the lth category; and El is the expected frequency (count) for the lth category. The range of χ² is between 0.000 to infinity. Compared with the critical value based on the degrees of freedom, a lower value indicates a better fitting. | |
| NFI | It compares the fitting of a proposed model to a baseline model, which usually represents a model of independence (i.e., no relationship between the variables). | NFI is the Normed Fit Index; χ2 nul is the Chi-Square for the null model; and χ2 model is the Chi-Square for the specified model. The range of NFI is from 0.000 to 1.000. NFI value above 0.900 is typically considered indicative of a good fitting. | |
| VIF | It quantifies how much the variance of an estimated regression coefficient increases when predictors are correlated. Moreover, it assesses multicollinearity in regression analysis. | VIF is the Variance Inflation Factor; and R2 j is the coefficient of determination obtained by regressing the jth independent variable against all other variables. VIF=1.000 means no correlation; 5.000<VIF<10.000 means moderate correlation; 1.000≤VIF≤5.000 means high correlation; and VIF>10.000 means very high correlation. | |
| CV | It measures the relative variability of a dataset compared to its mean. | CV is the coefficient of variation; σ is the standard deviation (SD); and μ is the mean of the dataset. A higher CV indicates greater variability relative to the mean. | |
| RMS | It measures the average of the squared differences (residuals) between the observed and predicted covariance matrices. | Where RMS is the Root Mean Square; Oi is the observed value for the ith observation; and Pi is the predicted value for the ith observation. A value of RMS closer to 0.000 suggests that the model adequately captures the relationships in the data. | |
| α | It measures the internal consistency and assesses how closely related a set of items are as a group. | α is the Cronbach’s Alpha; k is the number of items; δ2 Yg is the variance of the gth item; and δ2 Y is the variance of the total score. The range of α is between 0.000 and 1.000, with values above 0.700 generally being considered acceptable. | |
| ρA | It is another measure of internal consistency and is often preferred over Cronbach’s Alpha, because it does not assume equal item loadings. | ρA is the Dillon-Goldstein’s Rho; λg is the factor loading of item; and | |
| CR | It reflects the factors’ reliability based on the factor loadings and error variances. | CR is the Composite Reliability. CR value above 0.700 is considered acceptable. | |
| AVE | It indicates how much of the variance in the observed variables (factors) is accounted for by the latent variables. | AVE is the Average Variance Extracted. AVE≥0.500 indicates good convergent validity and AVE<0.500 indicates concerns about the factor’s validity. |
Table S2
Discriminant validity results of the Fornell-Larcker criterion."
| Factor | Climate migration | Economic strategies | Food insecurity | Irrigation management strategies | Organic- oriented strategies | Sustainable development- oriented strategies | Crop variety management strategies |
|---|---|---|---|---|---|---|---|
| Climate migration | 0.893 | ||||||
| Economic strategies | -0.090 | 0.915 | |||||
| Food insecurity | 0.237 | -0.119 | 0.722 | ||||
| Irrigation management strategies | -0.465 | 0.248 | -0.238 | 0.753 | |||
| Organic-oriented strategies | -0.330 | 0.180 | -0.244 | 0.503 | 0.795 | ||
| Sustainable development -oriented strategies | 0.316 | -0.429 | 0.144 | -0.560 | -0.386 | 0.711 | |
| Crop variety management strategies | 0.478 | -0.122 | 0.136 | -0.643 | -0.457 | 0.432 | 0.774 |
Table S3
Discriminant validity results of the Heterotrait-Monotrait Ratio (HTMT)."
| Factor | Climate migration | Economic strategies | Food insecurity | Irrigation management strategies | Organic- oriented strategies | Sustainable development- oriented strategies | Crop variety management strategies |
|---|---|---|---|---|---|---|---|
| Economic strategies | 0.095 | ||||||
| Food insecurity | 0.251 | 0.117 | |||||
| Irrigation management strategies | 0.581 | 0.278 | 0.274 | ||||
| Organic-oriented strategies | 0.392 | 0.201 | 0.261 | 0.671 | |||
| Sustainable-oriented strategies | 0.368 | 0.465 | 0.161 | 0.704 | 0.472 | ||
| Crop management strategies | 0.572 | 0.146 | 0.143 | 0.844 | 0.565 | 0.524 |
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