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Innovations in Groundwater Recharge

The operation of large canal irrigation systems in the Indo-Gangetic Plain and similar hydro-geological areas can be modified to recharge groundwater on a vast scale. This reduces the need for new dams and other storage structures.

The results of a 10-year study in Uttar Pradesh show that surplus monsoon water can be used to recharge underground aquifers and simultaneously provide farmers with better crop security.

Earthen irrigation systems can be transformed into highly productive region-wide groundwater recharge systems—at very little cost.

Lessons learned from a 10-year pilot project in Uttar Pradesh indicate a practical and low-cost way to conserve and rejuvenate falling groundwater reserves. Here, monsoon river flows are being channeled through earthen canals to irrigate wet-season crops. Seepage water from the canals and fields simultaneously recharges the underlying aquifers. As a result, declining water tables have been arrested, pumping costs for irrigation have been reduced and the region’s agricultural productivity has been improved. This approach has the potential to improve farmers’ livelihoods in areas that have hydro-geological characteristics similar to those of the western Indo-Gangetic Plain.

Putting this type of approach into action requires a shift in a State’s water policy and practice. Irrigation departments will have to move from supplying water only in the dry season to delivering adequate water during the monsoon, so that farmers can grow water-intensive crops, such as rice and sugarcane—where the water irrigates fields and simultaneously recharges groundwater aquifers. The water that is stored in the aquifers can then be pumped back up for a second post-monsoon cropping season. The advantages of this approach are that groundwater levels are maintained, farmers’ annual yields are increased, pumping costs are reduced and waterlogging is minimized.

The amount of water pumped by farmers from India’s aquifers is greatly exceeding natural recharge in many areas. In the western part of the Indo-Gangetic Plain, where the recharge approach described here was initiated, rainfall ranges between 650 and 1,000 mm annually, but only 200 mm naturally percolate through the soil layer to replenish underlying aquifers. Most of this rainfall, which is concentrated during the 3 months of the monsoon, does not have time to be absorbed into already saturated soil and so runs off—eventually flowing unused into the sea. If a fraction of this runoff could be stored underground through artificial recharge, the problem of declining water tables that plagues much of the region could be solved.

Recent research suggests that providing farmers with irrigation water during the monsoon offers a cost-effective option for harnessing this previously wasted resource to artificially recharge groundwater. If surplus river flows can be channeled through an unlined system to provide farmers with irrigation for monsoon crops, seepage water from the canals and fields will refill underlying aquifers (see figure 1). This stored water can then be pumped up by farmers during the dry season for a second crop. The resulting drawdown of the aquifers maximizes their storage potential for the next monsoon and prevents waterlogging. This conjunctive management of canal water and groundwater has proved productive and, above all, sustainable.

Providing canal water only during the monsoon season has a number of advantages beyond aquifer recharge. Farmers are no longer at the mercy of monsoon rains, which sometimes fail to provide enough water when and where it is needed. They are guaranteed sufficient water to irrigate both a monsoon and a post-monsoon crop.

Head-tail differences are minimized: during the monsoon, there is enough water for users at the tail end of the irrigation system, and there is still plenty to recharge the aquifer. During the dry season, since there is no canal supply, all the farmers have to pump water if they want to irrigate a post-monsoon crop. Since pumping costs farmers money, they use the water more efficiently.

Transforming irrigation systems into recharge systems

The research by Roorkee University, the Water and Land Management Institute (WALMI) of Uttar Pradesh, and the State’s Irrigation Department, in collaboration with the International Water Management Institute (IWMI), evaluated this ongoing experiment in large-scale recharge being carried out by the Government of Uttar Pradesh.

The recharge project involved the construction of a barrage across the river Ganga at Raolighat, which diverts 234 m3/sec of water into the Madhya Ganga Canal when the monsoon raises river flows. The Madhya Ganga Canal feeds the existing Upper Ganga Canal system and the newly constructed Lakhaoti Branch Canal system. This water is supplied to farmers, who use it to irrigate such water-intensive monsoon crops as paddy rice and sugarcane. The research documented how this diversion of surplus Ganga water during the monsoon season has affected groundwater levels, land use, cropping pattern, and the costs and benefits of agricultural operations—focusing specifically on the Lakhaoti Branch Canal system.

The research showed that the water table, which had been progressively declining, has been raised from an average of 12 m below ground level to an average of 6.5 m. A simulation of the groundwater system suggests that without the artificial recharge provided by the monsoon irrigation, the water table would have fallen to an average depth of 18.5 m below the surface during the course of the 10-year study period.

Farmers have benefited from the corresponding reduction in pumping costs and the improved cropping pattern. With the introduction of monsoon irrigation, the average net income has increased by 26% to Rs 11,640 per hectare. In addition, the recharge benefits other water users in the area—water demand for domestic purposes and industrial use are also met from recharged groundwater.

Saving on water storage infrastructure

The recharge effort described here can be duplicated using existing canal schemes of any size. The Lakhaoti is a medium-sized, unlined system, with a command area of about 206 thousand hectares, but any irrigation system in an area where there are viable aquifers and surplus monsoon water is a good candidate for this approach. The Indo-Gangetic Plain is ideal because it is underlain by a thick stratum of sandy soils, which readily holds and transmits groundwater.

The recharge approach has allowed the Government of Uttar Pradesh to increase agricultural production and provide farmers with irrigation water in previously existing dry pockets—without constructing dams or new reservoirs. In the area now covered by the Lakhaoti scheme, existing water rights precluded providing farmers with Ganga water for irrigation during the dry season. Building surface storage dams was not an option in this flat alluvial terrain. Even if suitable sites for such structures could be found, escalating costs of construction and stringent environmental requirements would be prohibitive.

These problems are not unique. They have troubled planners and policy makers for years. Practical and economically viable solutions are required, backed by sound science and proven results. The potential to build on earlier investments and use existing structures to avoid large capital outlays certainly merits consideration. It could save money, conserve vital natural resources and improve the livelihoods of poor farmers.

The most effective way to recharge groundwater in the climatic and hydro-geological conditions of the Indo-Gangetic Plain, this research suggests, is to modify the operation of unlined irrigation systems to carry surplus monsoon flows. Even in cases where canals are lined or partially lined, there will still be beneficial recharge—though not as much as from an unlined scheme.
This type of recharge effort is also cost-effective. The total cost of canal water at canal head (capital cost + operation and maintenance cost at 1990 prices) is Rs 0.3162 per m3. With each m3 of water bringing an average return of Rs 8,1 the canal water is an extremely good investment.

If this irrigation policy shift is put into action on a large scale, the socioeconomic impact can be potentially huge. It will improve farmers’ incomes, while helping save state expenditure on water infrastructure or dam construction, stabilizing power generation requirements, and lowering atmospheric emissions and environmental impacts.

A strategy of combining groundwater recharge through monsoon irrigation with appropriate electricity pricing and groundwater use regulations, has the potential to drastically improve the productivity and sustainability of farmers’ water use in areas where overpumping is currently endangering groundwater resources.

Reversing groundwater decline

Before the introduction of monsoon canal irrigation, withdrawal of groundwater in the area was exceeding recharge, and the water table was declining by an average of 0.5 m per year. In 1984, the average depth of the water table was 10 m below ground level; by 1988, when the recharge effort began, it had fallen to 12 m. After 10 years of providing monsoon irrigation, the depth to groundwater has been almost halved—the average for 1998 was 6.5 m below ground level. Water table depth below ground level for the years 1984 (before the project began) and 1998 (after 10 years of operation) are shown in figure 2.

Groundwater hydrographs were prepared for five observation wells located from head to tail of the Lakhaoti Branch Canal. In the head-reach villages they show that the water table fell progressively until 1988, when the recharge effort began. Here the artificial recharge had an almost immediate impact (see figure 3). In the tail-end villages, it has taken longer for the water table to rise. In one tail-end village, for example, the water table continued to decline until 1990, then remained constant until 1997, when it finally began to rise (see figure 4). The primary reason it has taken the tail reach areas longer to respond to the canal water recharge is incomplete infrastructure for water distribution in the tail reach.

The groundwater balance calculated for the Lakhaoti command area shows that in a normal year, rainfall recharge is 370 million m3. Canal and field seepage contributes approximately 328 million m3. Total recharge, without considering the lateral inflow of 63 million m3 from other aquifers, works out to 698 million m3. Net pumping for irrigation averages around 663 million m3 —leaving 35 million m3 to help raise depleted water tables. Once water tables have reached an optimal level (approximately 3 m below ground level), farmers will need to increase pumping to balance recharge and prevent water levels from increasing further.

Impact on farm budgets

When water tables drop, farmers’ pumping costs go up. After the introduction of the recharge effort, the groundwater level rose and consequently the cost of pumping fell. A simulation of the groundwater system shows that without the artificial recharge the water table would have dropped to an average depth of approximately 18.5 m over the 10-year study period. Lower groundwater tables would have increased the cost of pumping, and forced users to deepen wells and lower their pumping sets.

The cost of pumping with the water table at 18.5 m would have been Rs 0.465 per m3. Under current conditions, with groundwater at an average depth of 6.5 m, the cost of pumping groundwater is Rs 0.265 per m3—a savings of almost 50%. Considering that altogether farmers pump close to 900 million m3 (gross) annually, the amount saved in pumping costs comes to Rs 180 million per year.

Farmers’ incomes have also benefited from the increased production and from the better cropping pattern enabled by the monsoon irrigation. In the past, there was not always sufficient water for a post-monsoon crop; now, farmers are guaranteed enough water for two cropping seasons.

With the additional water provided by the monsoon irrigation, farmers have been able to expand the area irrigated. The canal irrigated area increased from 1,251 hectares for the 1988/89 season, to a maximum of 35,798 hectares in the 1997/98 season. The costs of cultivation, and gross and net benefits of major crops, with and without monsoon irrigation, are given in the table below.

Why is a policy change needed?

Over the years, State Irrigation Departments have aimed to store and distribute water to farmers in the dry season, so that at least two crops can be grown in a year. It is generally assumed that the monsoon brings enough water to go round and that farmers don’t need help. This is not always true. Monsoons are erratic and sometimes do not bring the promised rainfall.

Another fact is that the torrential monsoon rains bring vast amounts of water that are not needed for agriculture at that very moment. Most of the monsoon rains flood fields, filling rivers and streams that rush—unused—to the sea. This is the very water that could help the farmer year-round, if it could be diverted and its flows slowed down enough to percolate through to underground aquifers. Fast-flowing torrents wash away topsoil, and waterlogged fields are a farmer’s nightmare for such crops as pigeon pea that cannot tolerate excessively wet conditions.

From the farmers’ perspective, having better ‘crop security’ for monsoon crops by making irrigation water available to supplement an erratic supply of rain—and still having enough water stored in aquifers to grow another crop later—is an attractive proposition. But policy makers and water managers will have to clearly articulate the advantages and positive impact of the change if farmers are to be convinced. Farmers live with risks the year-round, so removing one of their main worries—the possibility of drought caused by monsoon failure—will give them the confidence to face their many other challenges.

Farmers will need to be convinced that this new approach will work for them. If they can be sure that their hard-earned pumps will continue to find water in the aquifers after the monsoon, that the pumps will not need to be lowered into ever-deepening borewells, and that the stable water table means lower power costs, then they will support changing cropping patterns as part of a new groundwater recharge strategy.

Consolidated farm budgets for Lakhaoti Branch command area with and without canal inputs

 

 
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Water Policy Briefing Issue January 2002 pdf 1073kb requires Adobe Acrobat™
This issue of Water Policy Briefing is based on research presented in the technical paper Artificial Recharging of Groundwater: An Experiment in the Madhya Ganga Canal Project, India by R. Sakthivadivel of the International Water Management Institute (IWMI) and A. S. Chawala formerly of the Water Resources Development and Training Centre (WRDTC), University of Roorkee, India. Readers interested in the details of this research are invited to read the full text of the technical paper online by clicking here or request a copy at the address given below. Questions and comments on this issue may be directed to Dr. R. Sakthivadivel c/o IWMI, Elecon, Anand-Sojitra Road, Vallabh Vidyanagar 388 001, Gujarat, India or iwmi-tata@cgiar.org.
 
Overview of project results-benefits to the region
  • 26% increase in average net income per ha for farmers.
  • Average depth to groundwater decreased from an average of 12m below ground level (1988) to an average of 6.5m (1998).
  • Annual pumping cost savings of Rs.180 million (900,000,000 m3 of water pumped each year).
  • Annual energy savings of 75.6 million kWh.
  • Canal irrigated area increased—from 1,251 ha (1988) to 37,108 ha (1996).
  • 15% increase in cropped area for rice—83 ha (1988) to 14,419 (1999)—with potential for further 30,000 ha. Irrigated sugarcane area increased by 1,000 ha.
  • Canal water input increased from 27,202,000 m3 (1988) to
    643,010,000 m3 in (1996).
  • Reduction of 50% in water conveyance losses with potential for further improvement.

 

How unused drainage canals can help maximize recharge

Recently published research from Punjab Agricultural University, Ludhiana suggests that the network of surface drains—that were constructed to control waterlogging and floods in the early 1950s but that are now rarely used—can be modified to catch monsoon rains and replenish falling groundwater tables in many areas of India. In effect, these unused drainage channels can be transformed into temporary reservoirs. Excess water not needed for irrigation can be diverted into these unused channels, where ‘check structures’ slow it for recharge. Click here to see figure >>

The research by S. D. Khepar and his colleagues shows how building check structures, at suitable intervals in the drainage canal, can increase the recharge capacity of a drain by three-and-a-half times over recharge under natural flow conditions. A model developed to estimate the recharge provides water managers with guidance for organizing canal water releases, while ensuring that there is no runoff at the outflow of the drain, under natural flow conditions and with check structures.

Using a combined approach—diverting monsoon water through earthen irrigation canals and the existing network of unused drainage canals offers several practical advantages. The most prominent is that the recharge ‘infrastructure’—earthen irrigation and drainage canals and groundwater aquifers—already exists, and can be modified at a very low cost, compared to planning and building dams, tanks or other water-storage facilities.

 
Indian regions/areas that can benefit
  • Where geology favors holding, storing, and allowing groundwater to be extracted, including areas with deep alluvial soils, sandy loams with low clay and kankar contents that have good potential to store water for later use.
  • Riverine systems with high river flows during the monsoon where flows are not used for crops, and run out to sea—conserving this floodwater is the main aim.
  • Locations where constructing a dam or building a surface reservoir causes environmental damage or flat alluvial terrain where surface storage dams cannot be built.
  • Locations where it is too expensive to build dams, or to transport water over long distances, where land cannot be allocated for storage, and the land values are high.
  • Areas with no soil salinity problems.
  • Places where the ground slope varies gradually and where it is not subject to flooding and/or waterlogging.
  • Command areas of existing canal irrigation systems where the canals can be better utilized for monsoon irrigation.
  • Places where accurate information on hydrogeology and groundwater movement are available, thus saving the cost of detailed surveys.
 
Direct benefits to farmers
  • Savings in pumping costs, and stable pumpset locations.
  • Better cropping patterns and operating conditions (availability of pumped groundwater for post-monsoon crop irrigation, and avoiding waterlogging).
  • Stable irrigation supply guaranteed by canal water supplements.
  • More annual income from additional rice and sugarcane.