
MENA Water Review · Visual story
Sanaa’s Water Crisis: How Unchecked Drilling Overwhelmed an Ancient Water System
In ancient times Yemen was among the world’s leaders in farming dry land and using water efficiently. With the arrival of modern drilling, its capital began to exhaust its water long before the war.
Running out of water is a gradual process, not a single event.
For more than a decade, Sanaa has often been identified as the capital most likely to run out of water first. The predicted dates have passed, including 2017, yet the city still has a water supply. The forecasts were not wrong about the resource.
A city of several million does not exhaust its aquifer overnight. Instead, the water table falls, water becomes more expensive, and access is rationed by price as well as by the pipe network. Households that once relied on a municipal connection buy from tankers. Tanker prices rise. Families further down the income scale buy less water and use water they would not otherwise have chosen. In practice, a city does not so much run out of water as divide into those who can still afford it and those who cannot.
Internal renewable water per person per year
Notes
The Falkenmark indicator treats 500 cubic metres per person per year as absolute scarcity. Yemen has roughly a ninth of that, among the lowest figures recorded anywhere.

Before the pump, none of these systems could be over-drawn.
Common accounts portray Yemen as careless with its water. The historical record suggests the opposite. On the mountainsides, farmers built stone terraces in their thousands. Some highland systems were first laid in the Bronze Age and are still in use. In the wadis, they practised spate irrigation, diverting the brief, violent floods that follow a storm across fields prepared to receive them.
All these systems share a design principle: each can use only water that has recently fallen as rain. A flood cannot be over-drawn. The rules that governed them, upstream before downstream and older fields before new ones, were enforced locally; in many spate systems that was the responsibility of the sheikhs of the wadi.
Interactive: choose a step, or use the arrows, to change the figure
Two hillsides under the same storm. The difference between them lies in what was built on the slope.
On the bare slope the water runs off quickly and carries the soil with it. On the terraced slope each wall holds it long enough to soak in.
Water held on the terraces can help recharge the ground below. A terrace that is not repaired collapses, and the soil behind it washes out in the next storm.
The well was, for each farmer, an entirely rational decision.
In the 1970s and 1980s, Yemeni men worked in the Gulf in very large numbers and sent billions of dollars home. Some of that money bought a diesel pump and a borehole. This is the crux of the account: for an individual farmer, the well was an unambiguously sound decision. It freed him from waiting for rain that might not come, allowed him to grow a cash crop rather than subsistence grain, and made his family more secure.
The resource he drew on, however, was shared and invisible. Customary rules addressed wells, including spacing and protection zones, but provided no precedent for unlimited extraction and sale from deep aquifers. What followed is the most familiar sequence in groundwater management and one of the hardest to arrest. As the water table falls, shallow wells fail. Those who can afford to drill deeper keep their water; those who cannot lose theirs. Depth becomes a proxy for wealth. Each new deep well lowers the table further, making it more necessary, rather than less, to drill deeper.
Interactive: choose a step, or use the arrows, to change the figure
In the early 1970s the water table in the Sanaa basin stood less than 30 metres below the surface.
Two decades of pumping had taken it below 150 metres.
New wells were being drilled 100 to 400 metres into the volcanic aquifer. From here the figures are drilling depths rather than measurements of the table itself.
Others were bored to depths of 300 to 500 metres in the sandstone aquifer.
A few reached 1,000 metres. The 2010 report put annual output from the Sanaa basin at around 200 million cubic metres, against an input of only 50 million.
Notes
The first two figures are water-table depths; the rest are drilling depths reported in 2010 by the World Bank-funded Sanaa Basin Water Management Project. Individual wells vary widely.
Qat provides income throughout the season, and is grown where water must be lifted.
Any account of water in Yemen must address qat, the mild stimulant leaf chewed socially by a large share of the adult population. Outside observers usually describe it as a national vice. It is more useful to understand qat as the crop that makes the most economic sense to grow. It is perennial: plantations can be kept productive for decades without replanting. Young shoots are picked two or three times a week during the season, and dry-season irrigation produces an off-season crop when prices are higher. Qat brings cash in on the very day of harvest, and an import ban shields it from the cheap imports that grain competes with.
Qat is also water-intensive, and it is grown where water has to be lifted. Estimates put qat at about 30 per cent of groundwater use, and in 2004 it covered nearly a fifth of the harvested irrigated area. In this sense, Yemen’s water problem shows what happens when the profitable use of a free resource and its sustainable use point in opposite directions.
Where Yemen’s water goes
Notes
Withdrawals for 2000 from FAO AQUASTAT; the qat share from the Sanaa Center. The two are measured on different bases, so the second bar is shown as a share of groundwater use rather than of the first bar.

Yemen has known for fourteen centuries what happens when the institutions fail.
East of Sanaa stand the remains of the Great Dam of Marib. Inscriptions credit Sabaean rulers with building it across Wadi Adhanah in the seventh century BCE. It was breached and repaired in 450, and again in 542. Around 570 CE, it broke for the last time. The irrigated land reverted to desert, and many of its people moved away, an event the Qur’an itself recalls.
It was the capacity to manage the water, rather than the water itself, that failed first.
- 7th c. BCE
The Great Dam of Marib
Sabaean rulers dam Wadi Adhanah. Its branching canals water the oasis fields of the kingdom of Saba.
- c. 570 CE
The dam fails for the last time
After breaches repaired in 450 and 542, the structure gives way for good. The irrigated land reverts to desert.
- Bronze Age on
Terraces and spate irrigation
Mountain terracing and wadi flood-spreading, governed by detailed customary water law, sustain rural populations on rainfall and floods alone.
- 1970s
Remittances and rigs
Money sent home from the Gulf, heavily subsidised diesel and new drilling rigs put a private well within reach of an ordinary farmer.
- 1980s–90s
The drilling boom
Groundwater use outruns customary control. The area under qat more than triples in twenty-five years.
- 2000s
The warnings become explicit
Output from the Sanaa basin is put at about 200 million cubic metres a year against an input of roughly 50 million (2010), and experts warn the capital could run short by 2017.
- 2015
War
Fuel scarcity cripples pumping and power. Across sixteen cities, 38 per cent of the water and sanitation assets assessed are affected (28 per cent damaged, 10 per cent destroyed), and civil servants’ salaries fall years into arrears.
- 2016–21
Cholera
The largest cholera outbreak of its time: more than 2.5 million suspected cases.
- 2019–26
The need does not recede
The UN counted 17.8 million people without adequate water, sanitation and hygiene in 2019. In June 2026, 14.4 million still required humanitarian assistance with them.
The war did not cause the crisis. It removed every remaining buffer.
Yemen’s water crisis was already decades old when the war escalated in 2015. Water is pumped in Yemen, and pumping requires fuel. Fuel scarcity and the collapse of the power grid left boreholes, treatment works and sewage plants struggling to operate. Networks were damaged, some directly, and civil servants went unpaid for years. Households fell back on tankers of uncertain quality and other unsafe sources.
The consequences became evident in October 2016, with the onset of one of the largest cholera outbreaks on record. Cholera is not an unusual disease. It spreads through food or water contaminated with the bacterium, and safe water and basic sanitation prevent it. That is precisely the infrastructure Yemen had been building but could no longer operate.
People in need of water, sanitation and hygiene assistance
Notes
The 2019 Humanitarian Needs Overview counted 17.8 million people as lacking adequate access and needing support to meet basic needs; the June 2026 WASH Insecurity Analysis reported 14.4 million requiring humanitarian assistance. Methods differ between the two assessments, so they are shown together to indicate scale rather than a trend.
Solar pumping removed the fuel bill that had limited extraction.
When fuel for pumps became scarce and expensive after 2015, Yemeni farmers adapted in a notable way: they turned to solar power. Markets for panels expanded rapidly, and solar pumping spread across the farms that could afford it. By most conventional measures, this was a positive development. Solar pumping is clean and resilient, and it works when fuel deliveries do not. It has kept water flowing through a war.
A diesel pump limits its own use: every hour of running costs money, so every farmer has a reason to stop. A solar pump, once installed, costs essentially nothing to operate, so the rational course is to run it whenever the sun is up.
Without the discipline of a fuel bill, solar pumping can exceed what diesel ever extracted, and local authorities do not regulate it. Yemen has thus replaced a polluting constraint on extraction with no constraint at all.
An optimistic conclusion would not be warranted. Groundwater is being drawn at more than twice the rate at which it refills, in a country whose real GDP per head has fallen by 58 per cent since 2015, with public institutions that can no longer deliver services and an unfinished war. But the picture is not uniform. Terrace rehabilitation restores rainwater capture and is labour-intensive, which, in a collapsed economy, is an advantage rather than a cost. Spate irrigation still functions in the wadis. At a local level, water management is often in the hands of water user associations, which are recognised by and under the authority of the state.
The underlying conclusion is that Yemen’s water problem is not, at root, hydrological. The country knew how to manage scarce water and did so for thousands of years, and the physical evidence of that knowledge still stands on its mountainsides. What broke was the link between the rules and the resource, when a technology arrived that allowed individuals to reach water that no rule covered.
Images: old city of Sanaa © Hamza Shiban (CC BY-SA 3.0); Haraz Mountains terraces © Rod Waddington (CC BY-SA 2.0); Great Dam of Marib © H. Grobe (CC BY-SA 3.0). Via Wikimedia Commons.
Sources
25 references
Groundwater figures for the Sanaa basin are estimates: the aquifer is not comprehensively monitored and the well count is itself an approximation. Depths after 1995 are drilling depths rather than measurements of the water table.
- Heffez, A. (2013), “How Yemen chewed itself dry”, The Washington Institute for Near East Policy, 23 July 2013.
- Sanaa Center, “Solar-powered irrigation in Yemen: opportunities, challenges and policies”.
- IRIN (now The New Humanitarian), “Capital city faces 2017 water crunch”, 23 March 2010.
- World Bank (2021), project appraisal document, Second Integrated Urban Services Emergency Project.
- World Bank, World Development Indicators, renewable internal freshwater resources per capita (cubic metres): Yemen, 2022 value.
- White, C. (2012), “Understanding water scarcity: definitions and measurements”, Global Water Forum, 7 May 2012.
- World Bank (2010), implementation completion report, Sanaa Basin Water Management Project.
- World Bank and GW-MATE (2003), Yemen: Rationalizing Groundwater Resource Utilization in the Sanaa Basin.
- UNDP (2022), A holistic approach to addressing water resources challenges in Yemen.
- Pietsch, D. and Mabit, L. (2012), “Terrace soils in the Yemen Highlands: using physical, chemical and radiometric data to assess their suitability for agriculture and their vulnerability to degradation”, Geoderma, doi:10.1016/j.geoderma.2012.03.027; abstract via edoc, University of Basel.
- FAO AQUASTAT, country profile: Yemen (2008 edition, archived).
- Conflict and Environment Observatory, “Groundwater depletion clouds Yemen’s solar revolution”, April 2021.
- PROTA (Plant Resources of Tropical Africa), Catha edulis, via Pl@ntUse, accessed October 2026.
- Ward, C. (2000), Yemen: CDR building block: qat, World Bank.
- Sanaa Center, “Qat expansion in Yemen’s war economy: water depletion and poisonous pesticides”, 2026.
- Stewart, R.T. (1978), “A dam at Marib”, Saudi Aramco World 29(2), March/April 1978.
- UNESCO World Heritage Centre, Landmarks of the Ancient Kingdom of Saba, Marib (archived).
- World Bank (2020), Yemen Dynamic Needs Assessment: Phase 3 (2020 Update).
- WHO EMRO, Cholera situation in Yemen, April 2021, via ReliefWeb (PDF).
- World Health Organization, Weekly Epidemiological Record, 21 September 2018, vol. 93, no. 38 (global cholera report for 2017), via ReliefWeb.
- UN OCHA (2019), Yemen: Humanitarian Needs Overview 2019.
- Global WASH Cluster, UNICEF and ECHO, WASH Insecurity Analysis (WIA): Yemen snapshot, June 2026, posted 24 August 2026.
- World Health Organization, cholera fact sheet, accessed September 2026.
- World Bank, Yemen country overview, accessed September 2026.
- United Nations in Yemen, “Being the change in Yemen: improving integrated water resources management for food security”, 23 March 2023.
Every figure and claim in this story rests on the references above. The stories list them here rather than marking them in the text; the country reports and hubs keep their inline markers.