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Water Management

The “water machine” of Bengal

A data-driven and policy-supported strategic use of aquifers for irrigation is needed to maximize their benefits
Science
15 Sep 2022
Vol 377, Issue 6612
pp. 1258-1259
For decades, millions of farmers in Bangladesh have been capturing more water than even the world’s largest dams. They did so simply by irrigating intensively in the summer dry season using water from shallow wells. The ability to use groundwater to irrigate rice paddies during the dry seasons (January to May) helped Bangladesh become food self-sufficient by the 1990s, which was no small feat for one of the most densely populated countries in the world. Researchers proposed that lowering of the groundwater table as a result of intensive irrigation practices in the dry season created conditions for recharge from monsoon rains (June to September), which then replenishes the groundwater (1). On page 1315 of this issue, Shamsudduha et al. (2) present a quantitative analysis of this depletion-replenish process and show that this recharge has indeed been happening at a large scale, in a process they call the Bengal Water Machine (BWM).
The name of the BWM pays homage to the Ganges Water Machine, which was coined in the 1970s. Both “water machines” describe a process in which the underground water table is lowered during dry seasons by human activities. This creates more space in the alluvial aquifer (made of loose sediments) for taking in heavy rainfall during the monsoon season. Such replenishment has the double benefit of helping farmers to grow dry-season crops and also increasing water storage capacity in underground aquifers for flood mitigation. In Bangladesh, Shamsudduha et al. observed an increase in annual intake, or “recharge,” after farmers started intensive irrigation from shallow wells (2011 to 2015) as compared with before (1976 to 1980). However, the authors also note that BWM is neither ubiquitous nor unlimited and can be affected by a number of factors, including local geology, land use, and year-to-year variations in rainfall.
The benefits of groundwater irrigation in the Bengal basin
GRAPHIC: K. HOLOSKI/SCIENCE
Although Bangladesh is endowed with fertile land and a favorable climate that allows cultivation throughout the year, the country has faced food shortages throughout its history. These can be attributed to the complex colonial history of the region, but it is undeniable that Bangladesh’s population density and the region’s vulnerability to cyclones and floods also played a role. After severe food shortages in the 1970s, Bangladesh embarked on a path toward agricultural intensification. Groundwater irrigation played a huge role in enabling this effort by allowing farmers to cultivate boro, a type of summer rice crop (3, 4). Affordable drilling of shallow tube wells, policy support for the import of cheap water pumps, and removal of bureaucratic control over pump installation have all contributed to a consistent increase in the area and production of boro rice (5, 6). In all, rice production increased from 9.9 million metric tons during the 1971–1972 season to 36.4 million metric tons during the 2018–2019 season. During the same period, the share of agricultural land use for boro cultivation also increased from 17.7 to 53.8%. However, more than 30 years after the removal of bureaucratic controls over pump installation, the government of Bangladesh reintroduced a pump permit system in 2019 to limit groundwater use (7). Without customizing these policies according to local aquifer and recharge conditions, the regulation may create unnecessary hurdles for farmers in search of affordable irrigation (8).
The findings of Shamsudduha et al. may help inform and develop region-specific guidelines for groundwater use. For example, their findings show that regions such as the Brahmaputra Basin, where the BWM seems to have the most potential, can be prioritized for groundwater use intensification. Conversely, restrictions for groundwater use can be tightened in the Ganges Basin and in Northwest Bangladesh, where the potential of the BWM has already reached its limit. This means that the BWM mechanism in those regions is already working at its maximum possible capability, with no room for additional recharge if the water tables are lowered further. In addition, regular upkeep of water bodies—including local streams, ponds, and canals—is needed to ensure that the BWM continues to function well. Using spatially explicit findings from Shamsudduha et al. to calibrate current groundwater use restrictions will ensure that the BWM continues to provide benefits.
The amount of energy needed to operate the water pumps must also be considered. Currently, roughly 1.3 million out of the 1.5 million water pumps in use are diesel operated, with the rest running on electricity generated from fossil fuels. In 2017 to 2018, the Bangladesh Petroleum Corporation sold 1.1 million metric tons of diesel to the agriculture sector, which ultimately accounted for 3.5 million metric tons of carbon dioxide (CO2) being emitted, or 4.3% of the country’s entire production-based CO2 emissions (9). As a net importer of fossil fuel, it is in the interest of Bangladesh’s energy security to develop a self-sufficient pathway to power the BWM. Replacing fossil fuel–reliant water pumps with solar-powered irrigation pumps is one such solution. The Bangladeshi government has started promoting solar-powered pumps, but advocates have demanded a faster pace in policy changes and public financing (10).
The long-term effect of climate change on the BWM is unclear. There is a lack of specificity for models of the impact of future climate change on how aquifers recharge under different conditions. There is some consensus about enhanced recharge in dry tropics because of increased precipitation (11, 12). However, future projections of recharge under climate change are lacking for humid and sub-humid tropics such as Bangladesh.
Induced recharge—such as that observed in the BWM—may also work in other aquifers with similar rainfall and geological conditions. Intensive groundwater use for irrigation in the dry season has created conditions for additional water storage in underground aquifers in parts of the Bengal Basin, with the double benefits of improving food security and flood mitigation. Similar high rainfall and alluvial aquifers also exist in the Ganga basins in eastern India and Nepal, where intensive groundwater irrigation can bring livelihood improvements, with positive cobenefits of additional induced recharge. Long-term groundwater monitoring along with policy support to farmers to make intensive use of groundwater will remain essential to unleash the benefits of BWM.

Acknowledgments

The author acknowledges the Swiss Agency for Development and Cooperation for their support of the project Solar Irrigation for Agricultural Resilience organized by the International Water Management Institute. Also acknowledged are support received from Transforming Agri-Food Systems in South Asia, and Mitigate+: Research for Low-Emission Food Systems.

References and Notes

1
R. Revelle, V. Lakshminarayana, Science 188, 611 (1975).
2
M. Shamsudduha et al., Science 377, 1315 (2022).
3
A. U. Ahmed, R. K. Sampath, Am. J. Agric. Econ. 74, 144 (1992).
4
A. R. Bell et al., Land Use Policy 48, 1 (2015).
5
M. Hossain, “The impact of shallow tubewells and boro rice on food security of Bangladesh,” discussion paper 00917 (International Food Policy Research Institute, 2009); https://bit.ly/3Q9g9A5.
6
R. Salim, A. Hossain, Appl. Econ. 38, 2567 (2006).
7
A. Mukherji et al., “Role of groundwater in agrarian change in West Bengal and Bangladesh: A comparative analysis—Final report” (Austrailian Centre for Inrernational Agrarian Research, 2021); https://bit.ly/3wJL4fv.
8
M. S. Islam, Austral. J. Asian Law 21, 47 (2021).
9
H. Ritchie et al., “CO2 and greenhouse gas emissions” (Our World in Data, 2020); https://bit.ly/3RoUPI5.
10
A. Mitra et al., “Solar irrigation in Bangladesh: A situation analysis report” (International Water Management Institute, 2021); https://doi.org/10.5337/2021.216.
11
A. Asoka et al., Geophys. Res. Lett. 45, 5536 (2018).
12
R. G. Taylor et al., Nat. Clim. Chang. 3, 374 (2012).

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Science
Volume 377 | Issue 6612
16 September 2022

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Published in print: 16 September 2022

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Acknowledgments

The author acknowledges the Swiss Agency for Development and Cooperation for their support of the project Solar Irrigation for Agricultural Resilience organized by the International Water Management Institute. Also acknowledged are support received from Transforming Agri-Food Systems in South Asia, and Mitigate+: Research for Low-Emission Food Systems.

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Aditi Mukherji [email protected]
International Water Management Institute, New Delhi Office, New Delhi, India.

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