Journal of Geographical Sciences >
Assessment on the sustainability of water resources utilization in Central Asia based on water resources carrying capacity
Liu Wenhua (1976-), Associate Professor, specialized in ecohydrology and sustainable water resources management. E-mail: liuwh@igsnrr.ac.cn |
Received date: 2022-10-14
Accepted date: 2023-05-17
Online published: 2023-10-08
Supported by
Strategic Priority Research Program of the Chinese Academy of Sciences(XDA19090120)
Strategic Priority Research Program of the Chinese Academy of Sciences(XDA19030104)
Youth Innovation Promotion Association of Chinese Academy of Sciences(2020056)
Situated in the hinterland of Eurasia, Central Asia is characterized by an arid climate and sparse rainfall. The uneven spatial distribution of water and land resources across the region has pressured economic and social development. An accurate understanding of Central Asia's water resources carrying capacity (WRCC) is vital for enhancing the sustainability of water resources utilization and guiding regional economic and social activities. This study aims to facilitate the sustainability of water resources utilization by evaluating the region's WRCC from the viewpoints of economic and technological conditions and social welfare. A concise yet effective model with relatively fewer parameters was established by adopting water resources data from the Food and Agriculture Organization (FAO) and socioeconomic data from the World Bank. The results indicated that the WRCC of all five Central Asian countries showed an increasing trend with improved water use efficiency from 1995 to 2020. Kazakhstan's WRCC was significantly higher than the other four countries, reaching 54.03 million people in 2020. The water resources carrying index (WRCI) of the five Central Asian countries varied considerably, with the actual population sizes of Turkmenistan and Uzbekistan highly overloaded. Although there has been a decrease in Central Asian countries’ WRCI between 1995 and 2020, water resources utilization problems in the region remain prominent. Based on the water resources carrying capacity evaluation system, to increase available water resources and improve production water use efficiency are key to address these issues. In light of this, this study offers practical and feasible solutions at the policy level: (1) The implementation of signed multilateral agreements on transboundary water resources allocation must proceed through joint governmental efforts. (2) Investments in advancing science and technology need to be increased to improve water use efficiency in irrigation systems. (3) The output of water-intensive crops should be reduced. (4) The industrial structure could be further optimized so that non-agricultural uses are the primary drivers of gross domestic product (GDP) growth.
LIU Wenhua , WANG Yizhuo , HUANG Jinku , ZHU Wenbin . Assessment on the sustainability of water resources utilization in Central Asia based on water resources carrying capacity[J]. Journal of Geographical Sciences, 2023 , 33(10) : 1967 -1988 . DOI: 10.1007/s11442-023-2161-3
Figure 1 Geographical location of Central Asia and spatial distribution of annual precipitation |
Table 1 Summary of the data used in this study |
Parameters | Temporal coverage | Temporal resolution | Source |
---|---|---|---|
Surface water produced internally | 1997, 2002, 2007, 2012, 2017, 2018 | Annual | FAO https://www.fao.org/aquastat/statistics/query/index.html |
Groundwater produced internally | |||
Overlap between surface water and groundwater | |||
Total external renewable water resources | |||
Total renewable water resources | |||
Environmental flow requirements | |||
Agricultural water withdrawal | |||
Industrial water withdrawal | |||
Municipal water withdrawal | |||
Domestic water withdrawal | 2002, 2018 | Annual | OECD https://issuu.com/oecd.publishing/docs/central_asia_water_management-web |
Population | 1990-2020 | Annual | The World Bank https://data.worldbank.org/ |
GDP | |||
Per capita GDP | |||
Precipitation | 1981-2020 | Annual | MSWEP product http://www.gloh2o.org/mswep/ |
Figure 2 A conceptual framework for water resources carrying capacity in Central Asia (a. full framework; b. detail on characterizing water resources carrying capacity using data from the Food and Agriculture Organization and the World Bank) |
Table 2 General water resource conditions in Central Asia during 1995-2020 from FAO (109 m3) |
KAZ | KGZ | TJK | TKM | UZB | |
---|---|---|---|---|---|
Surface water produced internally | 56.50 | 46.46 | 60.46 | 1.00 | 9.54 |
Groundwater produced internally | 33.85 | 13.69 | 6.00 | 0.41 | 8.80 |
Overlap between surface water and groundwater | 26.00 | 11.22 | 3.00 | 0.00 | 2.00 |
Total external renewable water resources | 44.06 | -25.31* | -41.55* | 23.36 | 32.53 |
Total renewable water resources | 108.41 | 23.62 | 21.91 | 24.77 | 48.87 |
Environmental flow requirements | 36.31 | 8.22 | 6.75 | 5.36 | 14.00 |
Available water resources | 72.10 | 15.40 | 15.16 | 19.41 | 34.87 |
Note: * The negative sign means the difference between the country's outbound and inbound water volume, i.e., the net outbound water volume. |
Table 3 Division criterion of the WRCI in Central Asia |
Basic types | Sub types | WRCI |
---|---|---|
Surplus | Highly surplus | <0.6 |
Moderate surplus | 0.6~0.8 | |
Lowly surplus | 0.8~1.0 | |
Critical | - | =1.0 |
Overloaded | Lowly overloaded | 1.0~1.2 |
Moderate overloaded | 1.2~1.4 | |
Highly overloaded | ≥1.4 |
Figure 3 Changes in mean annual precipitation over Central Asia for the period 1981-2020 |
Table 4 Segregated list of total renewable water resources in Central Asia along with their remarks and references (109 m3) |
Remark | KAZ | KGZ | TJK | TKM | UZB |
---|---|---|---|---|---|
Without external renewable water resources | 64.351 | 48.931 | 63.461 | 1.411 | 16.341 |
75.402 | 46.502 | 66.802 | 1.402 | 16.302 | |
62.443 | 54.004 | 64.005 | 1.406 | 12.207 | |
With external renewable water resources | 108.411 | 23.621 | 21.911 | 24.771 | 48.871 |
109.602 | 20.602 | 16.002 | 24.702 | 50.402 | |
100.508 | 20.588 | 15.988 | 24.728 | 50.418 | |
108.009 | 14.8010 | 21.9011 | 21.0012 | 50.00~60.007 |
Figure 4 Temporal trends in the population (a), GDP (b) and GDP per capita (c) in Central Asia from 1990 to 2020 |
Figure 5 Temporal trends of total water withdrawal in Central Asia from 1995 to 2020 (a) and the proportion of water withdrawal in the five countries in 2020 (b) |
Figure 6 Temporal trends of water use per GDP in Central Asia from 1995 to 2020 |
Figure 7 Temporal trends of WRCC (a) and WRCI (b) in Central Asia from 1995 to 2020 |
Table 5 The production water use per unit of GDP (m3/dollar) of TKM and UZB according to the change of the WRCI |
Year | TKM | Critical (1.0) | Lowly surplus (0.8) | Moderate surplus (0.6) | KAZ | KGZ | TJK |
---|---|---|---|---|---|---|---|
1995 | 9.59 | 7.60 | 6.04 | 4.48 | 1.34 | 5.89 | 8.14 |
2000 | 8.55 | 6.49 | 5.15 | 3.82 | 1.30 | 6.85 | 11.26 |
2005 | 3.28 | 2.32 | 1.84 | 1.36 | 0.38 | 3.36 | 4.38 |
2010 | 1.21 | 0.83 | 0.66 | 0.49 | 0.14 | 1.57 | 1.71 |
2015 | 0.76 | 0.53 | 0.42 | 0.31 | 0.14 | 1.11 | 0.98 |
2020 | 0.54 | 0.37 | 0.30 | 0.22 | 0.14 | 0.95 | 1.13 |
Year | UZB | Critical (1.0) | Lowly surplus (0.8) | Moderate surplus (0.6) | KAZ | KGZ | TJK |
1995 | 4.12 | 2.39 | 1.87 | 1.35 | 1.34 | 5.89 | 8.14 |
2000 | 4.10 | 2.32 | 1.81 | 1.30 | 1.30 | 6.85 | 11.26 |
2005 | 3.77 | 2.23 | 1.75 | 1.26 | 0.38 | 3.36 | 4.38 |
2010 | 1.02 | 0.64 | 0.50 | 0.36 | 0.14 | 1.57 | 1.71 |
2015 | 0.62 | 0.37 | 0.29 | 0.21 | 0.14 | 1.11 | 0.98 |
2020 | 0.93 | 0.53 | 0.41 | 0.29 | 0.14 | 0.95 | 1.13 |
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