Evaluating Whether Farmland Consolidation Is a Feasible Way to Achieve a Balance of Potential Crop Production in Southeastern Coastal China
Abstract
:1. Introduction
1.1. Exploitation-Oriented Route That Ensures No Reduction in the Area of Farmland
1.2. Upgrade-Oriented Route That Focuses on Improving the Quality of Exisiting Farmland
2. Materials and Methods
2.1. Study Area
2.2. Data Source and Processing
2.3. Methodology
2.3.1. Requisition Aspect: Loss of Potential Crop Production
2.3.2. Compensation Aspect: Potential Crop Production That Could Be Added through Farmland Consolidation
- (1)
- The Area of Farmland Intended to Be Consolidated
- (2)
- Potential Crop Production to Be Added through Quality Improvement
- (3)
- Potential Crop Production to Be Added through Quantity Increase
2.3.3. Index of the Balance of Potential Crop Production
3. Results
3.1. Loss of Potential Crop Production Due to Occupation by Construction
3.1.1. The Area and Quality of Farmland Occupied by Construction during the Planing Period
3.1.2. Loss of Potential Crop Production
3.2. Supplement of Potential Crop Production Root in Farmland Consolidation
3.2.1. Regions of Farmland Consolidation and the Area of Farmland to Be Consolidated in Wenzhou City
3.2.2. Targets of Farmland Consolidation in Wenzhou City
3.2.3. Supplement of Potential Crop Production by the Enhancement of Farmland Quality and the Increase of the Effective Area of Farmland
3.3. Index of the Balance of Loss and Supplement of Potential Crop Production
4. Discussion
4.1. Interpretation of the Findings
4.2. Policy Implications
- (1)
- Expand sources of built-up land supply and improve its efficiency. Regarding rapid economic development, it is assumed that the loss of farmland resources has become an inevitable result of urbanization, especially for the farmland with lower elevation and that slope around the city [2]. According to this study, it is impossible to achieve the balance of potential crop production merely through farmland consolidation for the economically developed counties. Therefore, reducing the occupation of farmland is important and necessary. In practice, however, there are ways to reduce the occupation of farmland that are worthy of attention. With regard to the rapid economic development of southern mountainous areas, to reduce the occupation of farmland for urban development in this area, the central government in China has implemented pilot projects for the development of sloping land in some regions since 2006. In 2011, it published the “Guidance on Comprehensive Development and Urbanization of Low-slope Hilly Areas” to promote urban build-up on land uphill and preserve high-quality farmland. This measure has played a significant role in preserving farmland in southern mountainous areas [6,53,54]. Unfortunately, this proposal has not been adequately implemented, due to considerations of ecological sensitivity, risks of geological disaster, and the cost of developing sloping land. According to this study, loss of potential crop production due to occupation by construction in Wenzhou city is high, and the government should consider the development of sloping land based on a comprehensive evaluation of resources, environmental carrying capacity, and suitability for the development of territorial space. In addition, improving the utilization efficiency of existing construction land to reduce the newly increased construction land area would be of benefit, and this can be implemented by revitalizing idle rural residential land, improving the utilization efficiency of urban inefficient industrial land, and strengthening the utilization level of urban underground spaces.
- (2)
- The potential to increase crop production through the quality improvement of farmland should be taken seriously. According to this study, although a balance of potential crop production can only be achieved through the quality improvement of farmland in economically developed counties, the amount of potential crop production that is added through the quality improvement of farmland is still relatively large, reaching more than 40% of the losses, and for Wenzhou city as a whole, the figure reached 76% (Table 4). That is, the potential to increase crop production through quality improvement of farmland is noteworthy and should be the focus. It is especially important for economically developed counties with a severe shortage of reserve farmland that cannot compensate for newly reclaimed farmland. Against the background of 40–46 million hectares of medium-to-low-yield farmland [32], we believe that the core of farmland protection policies lies in protecting farmland resources and improving the quality of the existing farmland, to ultimately ensure national food security. Additionally, according to this study, more attention should be paid to farmland with an elevation of between 50 m and 500 m in economically developed counties along the east coast of China.
- (3)
- The difference in potential crop production that is added by farmland consolidation between counties should be focused on in the adjustment of the RCBF policy. As mentioned above, there is a significant negative correlation between GDP and the index of the balance of potential crop production of each county in Wenzhou city (Figure 5). We believe that the potential index of the balance of potential crop production (“W”) is an important parameter in deciding whether to implement land reclamation and exploitation programs to expand farmland, or whether to strive for provincial adjustment or national overall planning in implementing or adjusting the RCBF policy, and it can be used as one of the bases for the determination of the project and the overall quantity.
4.3. Limitations of Our Study and Perspectives
5. Conclusions
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
- Xin, L.; Li, X. China should not massively reclaim new farmland. Land Use Policy 2018, 72, 12–15. [Google Scholar] [CrossRef]
- Liu, L.; Liu, Z.; Gong, J.; Wang, L.; Hu, Y. Quantifying the amount, heterogeneity, and pattern of farmland: Implications for China’s requisition-compensation balance of farmland policy. Land Use Policy 2019, 81, 256–266. [Google Scholar] [CrossRef]
- Zhao, H.; Zhang, H.; Miao, C.; Ye, X.; Min, M. Linking heat source–sink landscape patterns with analysis of urban heat islands: Study on the fast-growing Zhengzhou city in central China. Remote Sens. 2018, 10, 1268. [Google Scholar] [CrossRef] [Green Version]
- Deng, Z.; Zhao, Q.; Bao, H.X.H. The impact of urbanization on farmland productivity: Implications for China’s requisition-compensation balance of farmland policy. Land 2020, 9, 311. [Google Scholar] [CrossRef]
- Yang, B.; Ke, X.; van Vliet, J.; Yu, Q.; Zhou, T.; Verburg, P.H. Impact of cropland displacement on the potential crop production in China: A multi-scale analysis. Reg. Environ. Change 2020, 20, 97. [Google Scholar] [CrossRef]
- Chen, H.; Tan, Y.; Xiao, W.; Li, G.; Meng, F.; He, T.; Li, X. Urbanization in China drives farmland uphill under the constraint of the requisition–Compensation balance. Sci. Total Environ. 2022, 831, 154895. [Google Scholar] [CrossRef]
- Gao, R.; Chuai, X.; Ge, J.; Wen, J.; Zhao, R.; Zuo, T. An integrated tele-coupling analysis for requisition–compensation balance and its influence on carbon storage in China. Land Use Policy 2022, 116, 1060507. [Google Scholar] [CrossRef]
- Ke, X.; Zhou, Q.; Zuo, C.; Tang, L.; Turner, A. Spatial impact of cropland supplement policy on regional ecosystem services under urban expansion circumstance: A case study of Hubei Province, China. J. Land Use Sci. 2020, 15, 673–689. [Google Scholar] [CrossRef]
- Liu, Y. Introduction to land use and rural sustainability in China. Land Use Policy 2018, 74, 1–4. [Google Scholar] [CrossRef]
- Liang, C.; Jiang, P.; Chen, W.; Li, M.; Wang, L.; Gong, Y.; Pian, Y.; Xia, N.; Duan, Y.; Huang, Q. Farmland protection policies and rapid urbanization in China: A case study for Changzhou City. Land Use Policy 2015, 48, 552–566. [Google Scholar] [CrossRef]
- Shen, X.; Wang, L.; Wu, C.; Lv, T.; Lu, Z.; Luo, W.; Li, G. Local interests or centralized targets? How China’s local government implements the farmland policy of Requisition–Compensation Balance. Land Use Policy 2017, 67, 716–724. [Google Scholar] [CrossRef]
- Li, W.; Wang, D.; Liu, S.; Zhu, Y.; Yan, Z. Reclamation of Cultivated Land Reserves in Northeast China: Indigenous Ecological Insecurity Underlying National Food Security. Int. J. Environ. Res. Public Health 2020, 17, 1211. [Google Scholar] [CrossRef] [PubMed] [Green Version]
- Xiong, B.; Chen, R.; Xia, Z.; Ye, C.; Anker, Y. Large-scale deforestation of mountainous areas during the 21st Century in Zhejiang Province. Land Degrad. Dev. 2020, 31, 1761–1774. [Google Scholar] [CrossRef]
- Li, C.; Chen, L.; Liu, D.; Wei, J.; He, J.; Duan, X. The hidden risk in China’s cropland conversion from the perspective of slope. Catena 2021, 206, 105536. [Google Scholar] [CrossRef]
- Meyfroidt, P.; Rudel, T.K.; Lambin, E.F. Forest transitions, trade, and the global displacement of land use. Proc. Natl. Acad. Sci. USA 2010, 107, 20917–20922. [Google Scholar] [CrossRef] [PubMed] [Green Version]
- van Vliet, J. Direct and indirect loss of natural area from urban expansion. Nat. Sustain. 2019, 2, 755–763. [Google Scholar] [CrossRef]
- Chen, W.; Ye, X.; Li, J.; Fan, X.; Liu, Q.; Dong, W. Analyzing requisition–compensation balance of farmland policy in China through telecoupling: A case study in the middle reaches of Yangtze River Urban Agglomeration. Land Use Policy 2019, 83, 134–146. [Google Scholar] [CrossRef]
- Lu, S.; Qin, F.; Chen, N.; Yu, Z.; Xiao, Y.; Cheng, X.; Guan, X. Spatiotemporal differences in forest ecological security warning values in Beijing: Using an integrated evaluation index system and system dynamics model. Ecol. Indic. 2019, 104, 549–558. [Google Scholar] [CrossRef]
- Li, S.; Li, X. Global understanding of farmland abandonment: A review and prospects. J. Geogr. Sci. 2017, 27, 1123–1150. [Google Scholar] [CrossRef]
- Lin, L.; Ye, Z.; Gan, M.; Shahtahmassebi, A.; Weston, M.; Deng, J.; Lu, S.; Wang, K. Quality Perspective on the Dynamic Balance of Cultivated Land in Wenzhou, China. Sustainability 2017, 9, 95. [Google Scholar] [CrossRef]
- Lichtenberg, E.; Ding, C. Assessing farmland protection policy in China. Land Use Policy 2008, 25, 59–68. [Google Scholar] [CrossRef]
- Martellozzo, F.; Ramankutty, N.; Hall, R.J.; Price, D.T.; Purdy, B.; Friedl, M.A. Urbanization and the loss of prime farmland: A case study in the Calgary–Edmonton corridor of Alberta. Reg. Environ. Change 2015, 15, 881–893. [Google Scholar] [CrossRef]
- Song, W.; Pijanowski, B.C. The effects of China’s cultivated land balance program on potential land productivity at a national scale. Appl. Geogr. 2014, 46, 158–170. [Google Scholar] [CrossRef]
- Ormerod, S.J.; Marshall, E.J.P.; Gillian, K.; Rushton, S.P. Meeting the ecological challenges of agricultural change: Editors’ introduction. J. Appl. Ecol. 2010, 40, 939–946. [Google Scholar] [CrossRef]
- Norse, D.; Ju, X. Environmental costs of China’s food security. Agric. Ecosyst. Environ. 2015, 209, 5–14. [Google Scholar] [CrossRef]
- Wang, L.; Zheng, W.; Tang, L.; Zhang, S.; Liu, Y.; Ke, X. Spatial optimization of urban land and cropland based on land production capacity to balance cropland protection and ecological conservation. J. Environ. Manag. 2021, 285, 112054. [Google Scholar] [CrossRef]
- Yin, F.; Zhou, T.; Ke, X. Impact of cropland reclamation on ecological security in the Yangtze River Economic Belt, China. Sustainability 2021, 13, 12735. [Google Scholar] [CrossRef]
- Wu, X.; Xu, Z. Study on the transformation of cropland protection under the background of rehabilitation system. Resour. Sci. 2019, 41, 9–22. (In Chinese) [Google Scholar]
- Tang, L.; Ke, X.; Zhou, T.; Zheng, W.; Wang, L. Impacts of cropland expansion on carbon storage: A case study in Hubei, China. J. Environ. Manag. 2020, 265, 110515. [Google Scholar] [CrossRef]
- Leipnik, M.; Su, Y.; Lane, R.; Ye, X. Agriculture and Food Production in China and the U.S. In A Comparative Geography of China and the U.S.; Hartmann, R., Wang, J., Ye, T., Eds.; Springer: Dordrecht, The Netherlands, 2014; pp. 117–158. [Google Scholar]
- Han, L.; Meng, P.; Jiang, R.; Xu, B.; Zhang, B.; Chen, M. Logical root, pattern exploration and management innovation of balancing cultivated land occupation and reclamation in the new era: Based on the workshop “improvement methods and management innovation of balancing cultivated land occupation and reclamation in the new era”. China Land Sci. 2018, 32, 90–96. (In Chinese) [Google Scholar]
- Wu, Y.; Shen, X. Governance Transformation for Cultivated Land Protection in China: Provision, Regulation and Enabling. China Land Sci. 2021, 35, 32–38. (In Chinese) [Google Scholar]
- Griffiths, P.; Müller, D.; Kuemmerle, T.; Hostert, P. Agricultural land change in the Carpathian ecoregion after the breakdown of socialism and expansion of the European Union. Environ. Res. Lett. 2013, 8, 45012–45024. [Google Scholar] [CrossRef]
- Zumkehr, A.; Campbell, J.E. Historical U.S. Cropland Areas and the Potential for Bioenergy Production on Abandoned Croplands. Environ. Sci. Technol. 2013, 47, 3840–3847. [Google Scholar] [CrossRef] [PubMed]
- Gibson, G.R.; Campbell, J.B.; Zipper, C.E. Sociopolitical influences on cropland area change in Iraq, 2001–2012. Appl. Geogr. 2015, 62, 339–346. [Google Scholar] [CrossRef]
- van Vliet, J.; Eitelberg, D.A.; Verburg, P.H. A global analysis of land take in cropland areas and production displacement from urbanization. Glob. Environ. Change 2017, 43, 107–115. [Google Scholar] [CrossRef]
- Chen, R. The Analysis of Dynamic Balance Between Cultivated Land Supply and Demand of Wenzhou City. Ph.D. Thesis, Tongji University, Shanghai, China, 2007. (In Chinese). [Google Scholar]
- Zhang, G.; Wu, Y.; Zhao, Y. Physical suitability evaluation of reserve resources of cultivated land in China based on SOTER. Trans. Chin. Soc. Agric. Eng. 2010, 26, 1–8. (In Chinese) [Google Scholar]
- Ministry of Land Resources of the People’s Republic of China. Regulation for Gradation on Agriculture Land Quality; China Plan Press: Beijing, China, 2012. (In Chinese) [Google Scholar]
- Chen, Y.; Zhang, L.; Zhang, J.; Liu, H. Model for measuring cultivated land that could be non-agriculturally transformed based on crop productivity. J. Nat. Resour. 2013, 28, 450–458. (In Chinese) [Google Scholar]
- Zhang, H.; Li, X.; Huo, X.; Zhang, L. Study on the realistic potential of farmland consolidation on the theory of productivity—A case study on Suning County, Hebei Province. Res. Soil Water Conserv. 2011, 18, 202–206. (In Chinese) [Google Scholar]
- Ye, Q.; Chen, J.; Xiao, J.; Wei, W. Location choice for farmland consolidation based on constraints of ecology and non-agriculture land conversion. Trans. Chin. Soc. Agric. Eng. 2011, 27, 293–299. (In Chinese) [Google Scholar]
- Wang, J.; Yan, S.; Bai, Z.; Yu, L.; Guo, Y. Review on landscape patterns of land consolidation and the ecological effects. China Land Sci. 2012, 26, 87–94. (In Chinese) [Google Scholar]
- Jiang, G.; Zhang, R.; Ma, W.; Zhou, D.; Wang, X.; He, X. Cultivated land productivity potential improvement in land consolidation schemes in Shenyang, China: Assessment and policy implications. Land Use Policy 2017, 68, 80–88. [Google Scholar] [CrossRef]
- Bren D Amour, C.; Reitsma, F.; Baiocchi, G.; Barthel, S.; Güneralp, B.; Erb, K.; Haberl, H.; Creutzig, F.; Seto, K.C. Future urban land expansion and implications for global croplands. Proc. Natl. Acad. Sci. USA 2017, 114, 8939–8944. [Google Scholar] [CrossRef] [PubMed] [Green Version]
- Liu, S.; Dong, Y.; Li, D.; Liu, Q.; Wang, J.; Zhang, X. Effects of different terrace protection measures in a sloping land consolidation project targeting soil erosion at the slope scale. Ecol. Eng. 2013, 53, 46–53. [Google Scholar] [CrossRef]
- Deng, X.; Lian, P.; Zeng, M.; Xu, D.; Qi, Y. Does farmland abandonment harm agricultural productivity in hilly and mountainous areas? Evidence from China. J. Land Use Sci. 2021, 16, 433–449. [Google Scholar] [CrossRef]
- Liu, Y.; Zhou, Y. Reflections on China’s food security and land use policy under rapid urbanization. Land Use Policy 2021, 109, 105699. [Google Scholar] [CrossRef]
- Zhang, Z.; Meng, X.; Elahi, E. Protection of Cultivated Land Resources and Grain Supply Security in Main Grain-Producing Areas of China. Sustainability 2022, 14, 2808. [Google Scholar] [CrossRef]
- Zhi, J.; Cao, X.; Zhang, Z.; Qin, T.; Qu, L.; Qi, L.; Ge, L.; Guo, A.; Wang, X.; Da, C.; et al. Identifying the determinants of crop yields in China since 1952 and its policy implications. Agric. For. Meteorol. 2022, 327, 109216. [Google Scholar] [CrossRef]
- Foley, J.A.; Ramankutty, N.; Brauman, K.A.; Cassidy, E.S.; Gerber, J.S.; Johnston, M.; Mueller, N.D.; O’Connell, C.; Ray, D.K.; West, P.C.; et al. Solutions for a cultivated planet. Nature 2011, 478, 337–342. [Google Scholar] [CrossRef]
- Li, C.; Jin, X. Potential evaluation of requisition-compensation balance of arable land production capacity in the planning period based on quality improvement at county level. J. Nat. Resour. 2016, 31, 265–274. (In Chinese) [Google Scholar]
- Zhou, L.; Dang, X.; Mu, H.; Wang, B.; Wang, S. Cities are going uphill: Slope gradient analysis of urban expansion and its driving factors in China. Sci. Total Environ. 2021, 775, 145836. [Google Scholar] [CrossRef]
- Yang, C.; Xia, R.; Li, Q.; Liu, H.; Shi, T.; Wu, G. Comparing hillside urbanizations of Beijing-Tianjin-Hebei, Yangtze River Delta and Guangdong–Hong Kong–Macau greater Bay area urban agglomerations in China. Int. J. Appl. Earth Obs. 2021, 102, 102460. [Google Scholar] [CrossRef]
Administrative Region | Area | Quality (Land Use Index) | Loss of Production Capacity | Proportion |
---|---|---|---|---|
Municipal district 1 | 5674.10 | 1576–3145 | 85,600.43 | 32.63% |
Cangnan | 2460.77 | 1110–3031 | 36,134.00 | 13.78% |
Pingyang | 1428.67 | 1096–3031 | 20,218.06 | 7.71% |
Ruian | 3228.39 | 1177–2688 | 44,050.26 | 16.79% |
Taishun | 62.31 | 1373–2288 | 851.06 | 0.32% |
Wencheng | 451.21 | 867–3263 | 6103.89 | 2.33% |
Yongjia | 1885.00 | 1184–3526 | 28,690.82 | 10.94% |
Yueqing | 2639.43 | 1589–3469 | 40,670.43 | 15.50% |
Wenzhou | 17,829.88 | 867–3526 | 262,318.95 | 100% |
Administrative Region | Regions | Farmland to Be Consolidated |
---|---|---|
Municipal district 1 | 80 | 11,287.58 |
Cangnan | 53 | 29,657.29 |
Pingyang | 60 | 24,441.16 |
Ruian | 50 | 27,364.34 |
Taishun | 40 | 25,525.35 |
Wencheng | 45 | 23,269.03 |
Yongjia | 100 | 32,676.60 |
Yueqing | 69 | 20,372.43 |
Wenzhou | 497 | 194,593.77 |
Elevation | Municipal District 1 | Cangnan | Pingyang | Ruian | Taishun | Wencheng | Yongjia | Yueqing | Wenzhou | |
---|---|---|---|---|---|---|---|---|---|---|
e ≤ 50 m | Sd | 4585.33 | 12,135.98 | 9288.96 | 15,320.70 | 0.00 | 0.00 | 2641.88 | 11,841.63 | 55,814.48 |
PL | 2593.02 | 8875.98 | 5341.07 | 11,690.15 | 0.00 | 0.00 | 3026.77 | 8364.86 | 39,891.85 | |
Sja | 56.83 | 80.53 | −37.04 | 94.75 | 0.00 | 0.00 | 29.20 | 17.73 | 242.00 | |
PN | 880.14 | 1238.80 | −542.22 | 1425.49 | 0.00 | 0.00 | 474.50 | 291.85 | 3768.56 | |
PN + PL | 3473.16 | 10,114.79 | 4798.84 | 13,115.64 | 0.00 | 0.00 | 3501.27 | 8656.71 | 43,660.41 | |
50 m < e ≤ 300 m | Sd | 3265.71 | 15,482.10 | 11,505.00 | 8059.71 | 3665.01 | 7067.13 | 14,686.38 | 7720.89 | 71,451.93 |
PL | 3663.48 | 17,588.25 | 11,699.51 | 6024.96 | 3346.59 | 6972.58 | 12,068.12 | 5872.66 | 67,236.15 | |
Sja | 22.40 | 177.46 | 61.98 | 328.20 | 83.57 | 228.03 | 347.19 | 90.48 | 1339.31 | |
PN | 348.73 | 2616.87 | 935.13 | 4546.23 | 1253.62 | 3431.21 | 5353.28 | 1397.33 | 19,882.40 | |
PN + PL | 4012.21 | 20,205.12 | 12,634.64 | 10,571.19 | 4600.21 | 10,403.79 | 17,421.41 | 7269.99 | 87,118.55 | |
300 m < e ≤ 500 m | Sd | 2555.07 | 1873.52 | 3014.47 | 3661.76 | 13,022.48 | 9432.96 | 12,576.96 | 809.91 | 46,947.13 |
PL | 1728.83 | 1002.90 | 2424.03 | 2800.79 | 8236.03 | 8415.87 | 8555.30 | 228.88 | 33,392.64 | |
Sja | −58.38 | 8.77 | 81.69 | 155.99 | 313.78 | 341.16 | 421.57 | 9.19 | 1273.78 | |
PN | −906.75 | 119.36 | 1140.84 | 2108.01 | 4518.96 | 5109.07 | 6324.53 | 130.07 | 18,544.10 | |
PN + PL | 822.08 | 1122.27 | 3564.87 | 4908.80 | 12,754.99 | 13,524.94 | 14,879.84 | 358.95 | 51,936.73 | |
500 m > e ≤ 800 m | Sd | 881.47 | 165.69 | 597.63 | 205.63 | 7938.37 | 5895.51 | 2462.05 | 0.00 | 18,146.35 |
PL | 263.80 | 0.00 | 288.53 | 6.59 | 3489.83 | 3619.00 | 1090.39 | 0.00 | 8758.16 | |
Sja | 10.36 | 0.64 | −6.40 | 9.55 | 199.41 | 169.43 | 74.45 | 0.00 | 457.44 | |
PN | 150.03 | 8.53 | −81.63 | 118.51 | 2821.45 | 2436.65 | 1076.27 | 0.00 | 6529.81 | |
PN + PL | 413.83 | 8.53 | 206.90 | 125.10 | 6311.28 | 6055.66 | 2166.66 | 0.00 | 15,287.97 | |
e > 800 m | Sd | 0.00 | 0.00 | 35.10 | 0.00 | 899.50 | 873.42 | 309.32 | 0.00 | 2117.33 |
PL | 0.00 | 0.00 | 0.00 | 0.00 | 277.55 | 334.90 | 160.53 | 0.00 | 772.98 | |
Sja | 0.00 | 0.00 | −0.61 | 0.00 | 32.80 | 2.54 | 8.51 | 0.00 | 43.25 | |
PN | 0.00 | 0.00 | −7.20 | 0.00 | 453.06 | 34.45 | 117.05 | 0.00 | 597.35 | |
PN + PL | 0.00 | 0.00 | −7.20 | 0.00 | 730.61 | 369.35 | 277.58 | 0.00 | 1370.33 | |
Total | Sd | 11,287.58 | 29,657.29 | 24,441.16 | 27,364.34 | 25,525.35 | 23,269.03 | 32,676.60 | 20,372.43 | 19,4593.77 |
PL | 8249.13 | 27,467.13 | 19,753.14 | 20,522.49 | 15,350.01 | 19,342.36 | 24,901.12 | 14,466.40 | 150,051.78 | |
Sja | 31.21 | 267.40 | 99.64 | 588.48 | 629.56 | 741.16 | 880.92 | 117.40 | 3355.77 | |
PN | 472.15 | 3983.57 | 1444.92 | 8198.23 | 9047.08 | 11,011.38 | 13,345.64 | 1819.25 | 49,322.22 | |
PN + PL | 8721.28 | 31,450.70 | 21,198.06 | 28,720.72 | 24,397.09 | 30,353.74 | 38,246.76 | 16,285.65 | 199,374.00 |
Administrative Region | Loss of Potential Crop Production/PR | Supplement of Potential Crop Production by the Enhancement of Farmland Quality/PL | Supplement of Potential Crop Production by the Newly Increased Farmland Quality/PN | PL + PN | Potential Index of the Balance of Potential Crop Production/W |
---|---|---|---|---|---|
Municipal district 1 | 85,600.43 | 8249.13 | 472.15 | 8721.28 | 10.19% |
Cangnan | 36,134.00 | 27,467.13 | 3983.57 | 31,450.70 | 87.04% |
Pingyang | 20,218.06 | 19,753.14 | 1444.92 | 21,198.06 | 104.85% |
Ruian | 44,050.26 | 20,522.49 | 8198.23 | 28720.72 | 65.20% |
Taishun | 851.06 | 15,350.01 | 9047.08 | 24,397.09 | 2866.67% |
Wencheng | 6103.89 | 19,342.36 | 11,011.38 | 30,353.74 | 497.29% |
Yongjia | 28,690.82 | 24,901.12 | 13,345.64 | 38,246.76 | 133.31% |
Yueqing | 40,670.43 | 14,466.40 | 1819.25 | 16,285.65 | 40.04% |
Wenzhou | 262,318.95 | 150,051.78 | 49,322.22 | 199,374.00 | 76.00% |
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations. |
© 2022 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (https://creativecommons.org/licenses/by/4.0/).
Share and Cite
Li, C.; Jin, X.; Zhi, J.; Luo, Y.; Li, M.; Liu, W. Evaluating Whether Farmland Consolidation Is a Feasible Way to Achieve a Balance of Potential Crop Production in Southeastern Coastal China. Land 2022, 11, 1918. https://doi.org/10.3390/land11111918
Li C, Jin X, Zhi J, Luo Y, Li M, Liu W. Evaluating Whether Farmland Consolidation Is a Feasible Way to Achieve a Balance of Potential Crop Production in Southeastern Coastal China. Land. 2022; 11(11):1918. https://doi.org/10.3390/land11111918
Chicago/Turabian StyleLi, Chen, Xiangmu Jin, Junjun Zhi, Yao Luo, Mengni Li, and Wangbing Liu. 2022. "Evaluating Whether Farmland Consolidation Is a Feasible Way to Achieve a Balance of Potential Crop Production in Southeastern Coastal China" Land 11, no. 11: 1918. https://doi.org/10.3390/land11111918