Level of water stress: freshwater withdrawal as a proportion of available freshwater resources - Country Ranking

Definition: The level of water stress: freshwater withdrawal as a proportion of available freshwater resources is the ratio between total freshwater withdrawn by all major sectors and total renewable freshwater resources, after taking into account environmental water requirements. Main sectors, as defined by ISIC standards, include agriculture; forestry and fishing; manufacturing; electricity industry; and services. This indicator is also known as water withdrawal intensity.

Source: Food and Agriculture Organization, AQUASTAT data.

See also: Thematic map, Time series comparison

Find indicator:
Rank Country Value Year
1 Kuwait 3,850.50 2018
2 United Arab Emirates 1,667.33 2018
3 Saudi Arabia 1,000.00 2018
4 Libya 817.14 2018
5 Qatar 431.03 2018
6 Yemen 169.76 2018
7 Uzbekistan 168.92 2018
8 Turkmenistan 143.56 2018
9 Egypt 141.17 2018
10 Algeria 137.92 2018
11 Bahrain 133.71 2018
12 Syrian Arab Republic 124.36 2018
13 Sudan 118.66 2018
14 Pakistan 118.24 2018
15 Oman 116.71 2018
16 Jordan 100.08 2018
17 Tunisia 96.00 2018
18 Israel 95.94 2018
19 Sri Lanka 90.79 2018
20 Barbados 87.50 2018
21 Korea 85.22 2018
22 Malta 85.15 2018
23 Singapore 81.85 2018
24 Iran 81.29 2018
25 Eswatini 77.56 2018
26 India 66.49 2018
27 Tajikistan 64.48 2018
28 South Africa 63.56 2018
29 Lebanon 58.79 2018
30 Afghanistan 54.76 2018
31 Armenia 54.75 2018
32 Azerbaijan 53.73 2018
33 St. Kitts and Nevis 50.83 2018
34 Morocco 50.75 2018
35 Kyrgyz Republic 50.04 2018
36 Belgium 49.07 2018
37 Iraq 47.14 2018
38 Turkey 45.38 2018
39 Mexico 44.46 2018
40 China 43.22 2018
41 Spain 42.56 2018
42 Bulgaria 40.10 2018
43 Dominican Republic 39.55 2018
44 Japan 36.46 2018
45 Zimbabwe 35.41 2018
46 Germany 33.50 2018
47 Kenya 33.24 2018
48 Poland 33.22 2018
49 Kazakhstan 32.65 2018
50 Ethiopia 32.26 2018
51 Italy 30.00 2018
52 Indonesia 29.70 2018
53 Denmark 29.06 2018
54 Philippines 28.66 2018
55 Cyprus 28.29 2018
56 Timor-Leste 28.27 2018
57 United States 28.16 2018
58 Dem. People's Rep. Korea 27.74 2018
59 North Macedonia 25.27 2018
60 Somalia 24.53 2018
61 Czech Republic 24.19 2018
62 Cuba 23.94 2018
63 France 23.64 2018
64 Thailand 23.01 2018
65 Chile 21.62 2018
66 Mauritius 21.48 2018
67 Greece 20.48 2018
68 Trinidad and Tobago 20.33 2018
69 Ireland 20.04 2018
70 Puerto Rico 19.54 2018
71 Vietnam 18.13 2018
72 Malawi 17.50 2018
73 Estonia 17.41 2018
74 Netherlands 16.38 2018
75 United Kingdom 14.35 2018
76 St. Lucia 14.30 2018
77 Ukraine 13.87 2018
78 Haiti 13.38 2018
79 Mauritania 13.25 2018
80 El Salvador 13.21 2018
81 Tanzania 12.96 2018
82 Jamaica 12.47 2018
83 Moldova 12.43 2018
84 Portugal 12.32 2018
85 Senegal 11.81 2018
86 Madagascar 11.26 2018
87 Eritrea 11.18 2018
88 Argentina 10.46 2018
89 Burundi 10.19 2018
90 Dominica 10.00 2018
91 Uruguay 9.79 2018
92 Nigeria 9.67 2018
93 Austria 9.64 2018
94 Antigua and Barbuda 8.46 2018
95 Cabo Verde 8.43 2018
96 Nepal 8.31 2018
97 New Zealand 8.05 2018
98 Mali 8.00 2018
99 St. Vincent and the Grenadines 7.90 2018
100 Burkina Faso 7.82 2018
101 Hungary 7.65 2018
102 Venezuela 7.54 2018
103 Niger 7.45 2018
104 Grenada 7.05 2018
105 Ecuador 6.78 2018
106 Finland 6.64 2018
107 Peru 6.54 2018
108 Switzerland 6.50 2018
109 Slovenia 6.50 2018
110 Djibouti 6.33 2018
111 Ghana 6.31 2018
112 Serbia 6.26 2018
113 Rwanda 6.09 2018
114 Romania 6.01 2018
115 Uganda 5.83 2018
116 Myanmar 5.80 2018
117 Albania 5.76 2018
118 Guatemala 5.74 2018
119 Bangladesh 5.72 2018
120 Costa Rica 5.21 2018
121 Côte d'Ivoire 5.09 2018
122 Lao PDR 4.77 2018
123 Australia 4.66 2018
124 Honduras 4.62 2018
125 Belarus 4.58 2018
126 Luxembourg 4.33 2018
127 Chad 4.29 2018
128 Georgia 4.21 2018
129 Colombia 4.19 2018
130 Russia 4.12 2018
131 Suriname 3.95 2018
132 Canada 3.67 2018
133 Brunei 3.47 2018
134 Malaysia 3.44 2018
135 Sweden 3.43 2018
136 Mongolia 3.40 2018
137 Togo 3.39 2018
138 Guyana 3.30 2018
139 Zambia 2.84 2018
140 Nicaragua 2.69 2018
141 Bosnia and Herzegovina 2.66 2018
142 Lesotho 2.57 2018
143 Slovak Republic 2.39 2018
144 The Gambia 2.21 2018
145 Norway 2.05 2018
146 Botswana 2.02 2018
147 São Tomé and Principe 1.88 2018
148 Angola 1.87 2018
149 Paraguay 1.84 2018
150 Lithuania 1.83 2018
151 Mozambique 1.75 2018
152 Cameroon 1.56 2018
153 Croatia 1.50 2018
154 Guinea-Bissau 1.50 2018
155 Brazil 1.42 2018
156 Bhutan 1.41 2018
157 Guinea 1.37 2018
158 Belize 1.26 2018
159 Bolivia 1.18 2018
160 Latvia 1.08 2018
161 Cambodia 1.04 2018
162 Benin 0.98 2018
163 Panama 0.90 2018
164 Namibia 0.86 2018
165 Comoros 0.83 2018
166 Gabon 0.50 2018
167 Sierra Leone 0.50 2018
168 Iceland 0.39 2018
169 Central African Republic 0.34 2018
170 Fiji 0.30 2018
171 Liberia 0.26 2018
172 Dem. Rep. Congo 0.23 2018
173 Equatorial Guinea 0.18 2018
174 Papua New Guinea 0.13 2018
175 Congo 0.03 2018

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Development Relevance: The level of water stress can show the degree to which water resources are being exploited to meet the country's water demand. It measures a country's pressure on its water resources and therefore the challenge on the sustainability of its water use. It tracks progress in regard to “withdrawals and supply of freshwater to address water scarcity”, i.e. the environmental component of target 6.4. It also shows to what extent water resources are already used, and signals the importance of effective supply and demand management policies. It indicates the likelihood of increasing competition and conflict between different water uses and users in a situation of increasing water scarcity. Increased water stress, shown by an increase in the value of the indicator, has potentially negative effects on the sustainability of the natural resources and on economic development. On the other hand, low values of water stress indicate that water does not represent a particular challenge for economic development and sustainability.

Limitations and Exceptions: Water withdrawal as a percentage of water resources is a good indicator of pressure on limited water resources, one of the most important natural resources. However, it only partially addresses the issues related to sustainable water management. Supplementary indicators that capture the multiple dimensions of water management would combine data on water demand management, behavioural changes with regard to water use and the availability of appropriate infrastructure, and measure progress in increasing the efficiency and sustainability of water use, in particular in relation to population and economic growth. They would also recognize the different climatic environments that affect water use in countries, in particular in agriculture, which is the main user of water. Sustainability assessment is also linked to the critical thresholds fixed for this indicator and there is no universal consensus on such threshold. Trends in water withdrawal show relatively slow patterns of change. Usually, three-five years are a minimum frequency to be able to detect significant changes, as it is unlikely that the indicator would show meaningful variations from one year to the other. Estimation of water withdrawal by sector is the main limitation to the computation of the indicator. Few countries actually publish water use data on a regular basis by sector. Renewable water resources include all surface water and groundwater resources that are available on a yearly basis without consideration of the capacity to harvest and use this resource. Exploitable water resources, which refer to the volume of surface water or groundwater that is available with an occurrence of 90% of the time, are considerably less than renewable water resources, but no universal method exists to assess such exploitable water resources. There is no universally agreed method for the computation of incoming freshwater flows originating outside of a country's borders. Nor is there any standard method to account for return flows, the part of the water withdrawn from its source and which flows back to the river system after use. In countries where return flow represents a substantial part of water withdrawal, the indicator tends to underestimate available water and therefore overestimate the level of water stress. Other limitations that affect the interpretation of the water stress indicator include: difficulty to obtain accurate, complete and up-to-date data; potentially large variation of sub-national data; lack of account of seasonal variations in water resources; lack of consideration to the distribution among water uses; lack of consideration of water quality and its suitability for use; and the indicator can be higher than 100 per cent when water withdrawal includes secondary freshwater (water withdrawn previously and returned to the system), non-renewable water (fossil groundwater), when annual groundwater withdrawal is higher than annual replenishment (over-abstraction) or when water withdrawal includes part or all of the water set aside for environmental water requirements. Some of these issues can be solved through disaggregation of the index at the level of hydrological units and by distinguishing between different use sectors. However, due to the complexity of water flows, both within a country and between countries, care should be taken not to double-count.

Statistical Concept and Methodology: Proportion of total renewable water resources withdrawn is the total volume of groundwater and surface water withdrawn from their sources for human use (in the agricultural, municipal and industrial sectors), expressed as a percentage of the total actual renewable water resources. The terms water resources and water withdrawal are understood as freshwater resources and freshwater withdrawal. Water withdrawal is estimated for the following three main sectors: agriculture, municipalities (including domestic water withdrawal) and industries, at country level and expressed in km3/year. The total actual renewable water resources for a country or region are defined as the sum of internal renewable water resources and the external renewable water resources, also expressed in km3/year. The indicator is computed by dividing total water withdrawal by total actual renewable water resources minus environmental requirements and expressed in percentage points. Total freshwater withdrawal is the volume of freshwater extracted from its source (rivers, lakes, aquifers) for agriculture, industries and municipalities. It is estimated at the country level for the following three main sectors: agriculture, municipalities (including domestic water withdrawal) and industries. Freshwater withdrawal includes primary freshwater (not withdrawn before), secondary freshwater (previously withdrawn and returned to rivers and groundwater, such as discharged wastewater and agricultural drainage water) and fossil groundwater. It does not include non-conventional water, i.e. direct use of treated wastewater, direct use of agricultural drainage water and desalinated water. Total freshwater withdrawal is in general calculated as being the sum of total water withdrawal by sector minus direct use of wastewater, direct use of agricultural drainage water and use of desalinated water. Total renewable freshwater resources are expressed as the sum of internal and external renewable water resources. The terms “water resources” and “water withdrawal” are understood here as freshwater resources and freshwater withdrawal. Internal renewable water resources are defined as the long-term average annual flow of rivers and recharge of groundwater for a given country generated from endogenous precipitation. External renewable water resources refer to the flows of water entering the country, taking into consideration the quantity of flows reserved to upstream and downstream countries through agreements or treaties. Environmental water requirements (Env.) are the quantities of water required to sustain freshwater and estuarine ecosystems. Water quality and also the resulting ecosystem services are excluded from this formulation which is confined to water volumes. This does not imply that quality and the support to societies which are dependent on environmental flows are not important and should not be taken care of. Methods of computation of Env. are extremely variable and range from global estimates to comprehensive assessments for river reaches. Water volumes can be expressed in the same units as the total freshwater withdrawal, and then as percentages of the available water resources.

Periodicity: Annual