The sustainability of drinking water supply infrastructure remains a challenge in rural areas of low-and middle-income countries. Through this research to identify factors contributing to functionality, we analyzed monitoring data from ten non-governmental organization drinking water supply programs across nine sub-Saharan African and South Asian countries. Data were from 1,805 randomly selected water points, including tap stands, spring protections, rainwater collection systems, and hand pumps.
We found an impressive 92% of sampled water points constructed within the prior year were functional, versus only 79% of those constructed earlier (average 3.5 years, range: 1–12 years old).
Tap stands from piped water systems exhibited 74% lower odds of functioning than boreholes with hand pumps within the older construction sample. This disparity underscores the necessity of considering the suitability and reliability of various water supply systems in rural contexts.
As global efforts to expand piped water services align with international development goals, our results advocate for a nuanced approach. Higher water service levels offer undeniable benefits, but the accompanying technological, institutional, and financial requirements must be carefully weighed. Particularly in rural settings, where challenges of limited resources and infrastructure maintenance persist, comprehensive strategies are essential to mitigate risks and maximize the effectiveness of water supply interventions.
Read the full Open Access paper here:
Murray, A. L., Stone, G., Yang, A. R., Lawrence, N. F., Matthews, H., & Kayser, G. L. (2024). Rural water point functionality estimates and associations: Evidence from nine countries in sub-Saharan Africa and South Asia.Water Resources Research, 60, e2023WR034679. https://doi.org/10.1029/2023WR034679
By Victor Dang Mvongo, MSc, a PhD student at the University of Dschang (Cameroon) and an independent consultant in WASH. He conducted the work featured in this blog at the Faculty of Agronomy and Agricultural Sciences.
Handpumps, the most common rural water supply equipment in sub-Saharan Africa, are a symbol of the sustainability issue facing rural water services. According to Macarthur (2015), handpumps are a lifesaver for 184 million people living in rural sub-Saharan Africa. Sub-Saharan African statistics on handpumps’ functionality indicate that 36% of them are broken, with country-level rates varying from 10% to 65% (RWSN 2009).
In Cameroon, little data are available on the functionality of the handpump. However, Deal and Furey (2019) estimate that 32% of handpumps are non-functional. Thus, for the impacted rural areas, this means that the anticipated returns on investment—better health, nutrition, and education—are jeopardized. In order to mobilize the necessary national and international efforts in the region, this study intends to give local information on the functionality of handpumps in the Mvila Division (Southern Region of Cameroon).
This blog is part of a four-part series covering the presentations given at the 11th Zambia Water Forum and Exhibition. The event, themed “Accelerating Water Security and Sanitation Investments in Zambia: Towards Agenda 2023 through the Zambia Water Investment Programme”, lasted three days.
Our blog series takes a focused look at the presentations and discussions that revolved around “Addressing Rapid Hand Pump Corrosion in Zambia – Stop the Rot!”, which was co-convened by UNICEF and WaterAid, together with Ask for Water GmbH and the RWSN, hosted by Skat Foundation.
Cover photo: Red, iron-rich water being pumped. Photo: WaterAid Uganda
Second session:
The role of galvanized pipes in the corrosion and failure of hand pumps
Empowered Communities Helping Others (ECHO) has been implementing a safe water project since 2020. This is a Water Sanitation and Hygiene (WASH) project, whose main intervention is borehole rehabilitation which is implemented in rural parts of Zambia’s Western and Central Provinces, in collaboration with the Local Authority. In practice, the need to rehabilitate a borehole arises when a functioning borehole presents usage problems such as non-production of water, worn out parts such as pipes, rods, handles, chains, cylinders, water chambers, pedestal, head assembly, bearings, etc.
Since 2020, ECHO has rehabilitated a total of about 850 boreholes in Central and Western Zambia, benefiting a total of about 255,000 people.
It was found that rehabilitating a borehole can be more economical than constructing a new one. It is simpler and faster and can be an appropriate solution in an emergency because it doesn’t require things like mobilizing a drilling rig. However, if the rehabilitated borehole is to be used for a long time, it is important to estimate its life expectancy.
The rehabilitation option chosen depends on the conditions of the existing borehole, the causes of the damage, the technical and logistic options, and the existing alternatives such as the construction of a new water point.
According to the severity of the borehole problems, the work requirements may vary from a simple repair at the surface to re-equipment.
For the project, all GI pipes are replaced with new PVC ones. This is done in order to prevent and reduce iron contamination (as a result of corrosion) which from the past four years we have observed is a contributing factor to borehole failure and abandonment
The main observed sources of iron are:
▪ From natural sources in the aquifer
▪ From pump components such as steel casings and galvanized pipes.
▪ In other instances, a combination of both has been observed to be possible. ▪ Within 3 to 6 months of installing hand pumps with galvanized material, pipes and rods have been found to be heavily corroded.
▪ When corrosion is the main source of iron, iron concentrations reduce drastically when water is pumped out and fresh recharge is allowed. If iron concentrations remain high throughout during continued pumping, the case has been that it is likely the iron is coming from the aquifer.
Experiences on hand pump corrosion
Hand pumps with GI pipes, sometimes only a year or two old have corroded, and people have returned to unprotected water sources. Water with pH below 6 has been observed to have corroded pipes. High iron concentrations in handpumps have been a usual occurrence this has been observed through regular water quality testing and evaluating the change in iron concentration over the period of our operations. Stainless steel pipes and rods had corrosion rates lower than galvanized iron (GI) pipes and rods.
Experiences on hand pump corrosion
The brown or reddish color is observed in the morning when the pumps had not been used during the night
However, groundwater has been observed to hold significant concentrations of iron but appears clear and colorless. When this water is pumped out after being exposed to the atmosphere, the color changes to red/brown.
Figure 3: Sampled on Friday 2nd June 2023 in Central Province.
General complaints recorded from communities:
Within weeks and months of installation, communities would begin to complain about water quality. These complaints range from metallic taste, odor, and the appearance of water. Also, the communities would report discoloration of water and cloths and highly turbid water.
All these result in people abandoning the water point and going back to unprotected alternative water sources.
Positive observations
The use of uPVC pipes and stainless-steel adapters has so far shown positive results in reducing iron contamination. After switching from galvanized pipes to UPVC, the communities have observed reduced to no brown or reddish color in the water. uPVC pipes last long, so you won’t have to worry about replacing them anytime soon. Since uPVC is non-porous, uPVC pipes help by preventing any contamination from occurring. uPVC is resistant to corrosion as it is not susceptible to chemical and electrochemical reactions, so there are better option in controlling iron contamination. The use of uPVC pipes and stainless-steel adapters has so far shown positive results in reducing iron contamination
Figure 4: Riser pipe removal and water quality testing for an installation that was less than six months old by ECHO.
What we are advocating for:
▪ Stakeholders should address the handpumps with corrosion problems as a priority in order to guarantee the water quality we supply to the people.
▪ Testing boreholes that present iron contamination to determine whether the source of iron is from the aquifer or from corrosion. This will provide the best options for the right material to equip the water point with
▪ Competent borehole drilling and rehabilitation supervision should be ensured so that all standards and specifications are adhered to.
▪ Regular water quality analysis is undertaken, and critical parameters are tested to address problems such as corrosion and other related problems that shorten the life span of a hand pump
You are invited to access the presentations HERE, along with the session’s concept and report. If you would like to dive deeper into the enriching exploration of water challenges and solutions through the Stop the Rot initiative, visit this page.
About the author:
Annie Kalusa – Kapambwe presenting at at ZAWAFE 2023
Annie Kalusa is an accomplished development practitioner and administrator. Currently working for a local Zambian NGO Empowered Communities Helping Others (ECHO) in Zambia, focusing on improving the wellbeing of Vulnerable Rural Communities. Her areas of focus are climate resilient Water Sanitation and Hygiene (WASH). She is currently developing her thesis on Rural Agriculture Practices and Mechanisms for Water Resource Management.
This blog is part of a four-part blog series highlighting the presentations delivered during the 11th Zambia Water Forum and Exhibition. The event, themed “Accelerating Water Security and Sanitation Investments in Zambia: Towards Agenda 2023 through the Zambia Water Investment Programme”, lasted three days.
Our blog series takes a focused look at the presentations and discussions that revolved around “Addressing Rapid Hand Pump Corrosion in Zambia – Stop the Rot!”, which was co-convened by UNICEF and WaterAid, together with Ask for Water GmbH and the RWSN, hosted by Skat Foundation.
Third session:
The journey towards reducing the effects of rapid corrosion in Kalumbila District.
Kalumbila District is a district in the North-Western Province of Zambia. It has two major mines namely Lumwana and Kalumbila Mines.
With a population of over 170,000, the district has about 300 water points (boreholes and protected wells equipped with handpumps).
Rapid handpump corrosion has been a problem since the district was created in 2015. One of the interventions that the district has undertaken has been iron removal filters (to remove iron from pumped water), although these have not been sustainable.
Figure 1: Location of Kalimbula District
In every program of drilling of boreholes about 40% of boreholes were abandoned within one year after handover due to rapid corrosion.
We started looking for a solution to this problem. We found that iron filters were used but were not sustainable.
Figure 2: Handpump evaluation
One of the interventions that the district has undertaken has been iron removal filters (to remove iron from pumped water), although these have not been sustainable. In Kalumbila District it was found, that in every borehole programme, about 40% of the handpumps installed were abandoned due to high iron content, with some boreholes being abandoned as early as three months after construction and commissioning.
Projects
In 2017 UNICEF supported Kalumbila district in the drilling of 23 boreholes and rehabilitation of 15 water points.
In 2018 JICA also supported Kalumbila district with rehabilitation of 77 water points using uPVC pipes with stainless steel adapters. It is from these projects that we learnt a lot of important lessons and made recommendations to the D-WASHE committee. No water point was abandoned after one year of handover Kalumbila district decided to suspend the use of galvanised iron (GI) pipes and recommended the use of stainless steel and uPVC pipes for Indian Mark II and Afridev hand pumps.
Lessons learnt
It is from these two projects that we learnt a lot of lessons, and we told ourselves never to keep quiet. From these two projects, we observed that no water point was abandoned after one year of handover. We saw a solution – why continue to use GI pipes when there was a solution. So we made recommendations to the D-WASHE committee. After this, Kalumbila district decided to suspend the use of galvanised iron (GI) pipes and recommended the use of stainless steel and uPVC pipes for India Mark II and Afridev hand pumps. We have discovered that handpumps with stainless steel riser pipes do not require frequent repair and maintenance whereas sometimes the GI pipes would require replacement every six months. For the past four years, those handpumps remain working.
Our challenges include a lack of funding for the rehabilitation of boreholes affected by rapid corrosion. Further, some stakeholders have not supported the districts fully.
Recommendations
Stakeholders at the national level take an interest in order to address this issue of rapid corrosion.
The use of materials that are environmentally friendly without change of properties when they come into contact with aggressive water (i.e. materials such as stainless steel and uPVC).
There is capacity building of all Area Pump Menders (APMs) in Afridev hand pumps.
All hand pumps that have galvanised iron (GI) riser pipes are to be rehabilitated.
You are invited to access the presentations HERE, along with the session’s concept and report. If you would like to dive deeper into the enriching exploration of water challenges and solutions through the Stop the Rot initiative, visit this page.
About the author:
Daniel Shimanzapresenting at ZAWAFE 2023
Daniel Shimanza is a Zambian Citizen who has worked in the water sector for more than 6 years. He worked on many water supply projects in Kalumbila district, Zambia in collaboration with GRZ, NGOs such as UNICEF, and World Vision. He has a passion for the improvement of access to clean water supply for people living in rural areas. He’s championing a campaign to reduce the effects of rapid corrosion in Kalumbila district by using alternative materials such as stainless steel pipes, PVC pipes, Iron Filters, and more. He holds a Diploma in Water Engineering from NRDC and currently pursuing a Bachelor of Civil Engineering from the Copperbelt University.
This blog is part of a four-part series covering the presentations given at the 11th Zambia Water Forum and Exhibition. The event, themed “Accelerating Water Security and Sanitation Investments in Zambia: Towards Agenda 2023 through the Zambia Water Investment Programme”, lasted three days.
Our blog series takes a focused look at the presentations and discussions that revolved around “Addressing Rapid Hand Pump Corrosion in Zambia – Stop the Rot!”, which was co-convened by UNICEF and WaterAid, together with Ask for Water GmbH and the RWSN, hosted by Skat Foundation.
This blog is part of a four-part series covering the presentations given at the 11th Zambia Water Forum and Exhibition. The event, themed “Accelerating Water Security and Sanitation Investments in Zambia: Towards Agenda 2023 through the Zambia Water Investment Programme”, lasted three days.
Our blog series takes a focused look at the presentations and discussions that revolved around “Addressing Rapid Hand Pump Corrosion in Zambia – Stop the Rot!”, which was co-convened by UNICEF and WaterAid, together with Ask for Water GmbH and the RWSN, hosted by Skat Foundation.
Cover Photo: Removal of corroding riser pipe in Hoima District, Uganda in 2012 (source: Larry Bentley). In 2018 the Government of Uganda issued a directive to prevent further use of galvanised iron riser pipes throughout the country.
First session:
History of the Rapid Hand Pump Corrosion Problems in Zambia and Potential Next Steps
In Sub-Saharan Africa (SSA), an estimated 200 million people rely on a handpump for their main source of drinking water. They most likely use about 700,000 handpumps (Danert, 2022). Although the popularity of other technologies is growing, handpumps are likely to remain important in the region for decades to come, particularly in areas that are remote or with low population density. Unfortunately, many handpump services perform poorly or fail prematurely due to technical or installation defects with the borehole or the pump, as well as weaknesses with operation and maintenance or financial constraints.
In Zambia, it has been estimated that handpumps are the main source of drinking water for 19% of the urban and 32% of the rural population. It is worth to highlight that all metallic components that are submerged in water, or move in and out of water will eventually corrode, and so corrosion must be considered as part of the long-term maintenance of water wells with handpumps (or motorised pumps).
About rapid handpump corrosion
Rapid handpump corrosion occurs when aggressive groundwater reacts with galvanised iron (GI) riser pipes and rods of a handpump, and the India Mark II in particular. The materials corrode, with the pumped water becoming bitter in taste, with an unpleasant smell and a rusty colour. This not only renders the water unfit for drinking from a user perspective but also considerably reduces the pump lifespan. In Zambia, the main cause of rapid handpump corrosion is contact between groundwater with a pH of less than 6.5 and GI pipes and rods. However, salinity is also a problem in some parts of the country and can result in rapid corrosion too.
The use of alternative materials to GI, particularly stainless steel (SS) riser pipes and rods and uPVC rider pipes fitted with stainless steel connectors, can prevent rapid handpump corrosion. While rapid handpump corrosion was documented in West Africa in the late 1980’s ((Langenegger, 1989), and actions to prevent it have been taken in some places, the phenomenon still occurs in over 20 countries in sub-Saharan Africa. Zambia, with an estimated 22,000 handpumps in use, serving 32% of the population with their main drinking water supply, is among these countries.
Figure 1: Soil reaction map (pH) map of Zambia, 2014. (Shitumbanuma et all, 2021)
Figure 2: Zambia’s Agro-Ecological Zones (1987) and the 10 Provinces (Makondo & Thomas, 2020)
Figure 3: History of efforts in Zambia in relation to rapid handpump corrosion – Overview
In Zambia, while the geographical extent of aggressive water is not fully understood by water sector professionals, it has been documented and explained with respect to soils. A Soil Survey by the Mount Makulu Research Station from 1990 presents the situation clearly, with extreme soil acidity in the north, and soil acidity in the central parts of the country. Further, in Zambia the traditional Chitemene – ‘slash and burn’ – method of cultivation in the high rainfall region has been used since time immemorial to neutralise low pH in soils in order to cultivate crops. Leaching from these highly acidic soils affects the pH of the groundwater.
The problem of rapid corrosion in handpumps in Zambia has been known for more than 30 years (Pitcher, 2001) and is well documented, including in the following:
The Central Province Rural Water Supply Project (CPRWSP) (1985 – 1996) – which installed 564 handpumps with stainless steel riser pipes rather than using GI to prevent rapid corrosion.
The North-Western Province Rural Water Supply and Sanitation Project (2004 – 2009) – over 350 handpumps were installed with stainless steel riser pipes, also in response to the same issue.
In Luapula Province under the Japan International Cooperation Agency (JICA)-supported Groundwater Development Project (2007 – 2010), some Afridev handpumps with uPVC riser pipes were installed. The project rehabilitated existing, corroded handpumps which the community had previously abandoned. Replacing the GI pipes with uPVC stopped the iron problem, indicating that in these boreholes, using iron pipes had been the cause of corrosion. Iron removal plants were also installed on some boreholes.
However, while solutions were implemented at scale in the aforementioned projects in Central and North-Western Provinces, as well as the study in Luapula, the use of GI riser pipes and rods still continued in subsequent projects in the same areas.
Some stepbacks
There was a change in the ministry responsible for drilling works. The period 1985 – 1996 saw borehole drilling under the Department of Water Affairs, while the Department of Infrastructure and Support Services under the Ministry of Local Government and Housing took on this role after it had been created in 1995.
National Guidelines for Sustainable Operation and Maintenance of Handpumps in Rural Areas (MLGH, 2007) includes neither aggressive water as a criterion for handpump selection nor the use of stainless steel riser pipes, and so the use of GI pipes in aggressive water as the cause of the ensuing rapid corrosion was in effect further supported.
Initiatives undertaken in the last 10 years
Under the SOMAP 2 project (2012 – 2013), the JICA-supported programme carried out pipe replacement of GI at 20 sites in four provinces (Luapula, Copperbelt, Central and the North Western) whereby GI pipes were removed, the boreholes flushed and then installed with uPVC pipes. The replaced handpumps performed well without the water turning rusty, and the communities continued to draw water from them, whereas previously they had been abandoned.
UNICEF also carried out pipe replacement in Mansa and Milenge districts of Luapula Province. In the study, India Mark II handpumps GI pipes at 45 sites were replaced with uPVC riser pipes. After the pipe replacement of GI riser pipes, the community used the handpumps that had previously been abandoned, with unsafe water sources being used instead. The pipe replacement study was successful, with the water users returning to previously abandoned boreholes which had clear, rust-free water.
There is some evidence of other projects and organisations starting to use either stainless steel riser pipes, or uPVC riser pipes with stainless steel connectors in their projects, but documentation is limited. While stainless steel riser pipes have been used effectively, there are also some outstanding technical issues – particularly in relation to the removal of narrower diameter riser pipes, which require suitable tools that are not in the standard India Mark II toolkit. Further, the use of uPVC pipes has also been found to be problematic, as they need to be cut on removal and cannot easily be re-threaded. However, at least one NGO in Zambia has been using an alternative, comprising uPVC with stainless steel couplers which is available on the Zambian market. A further complication is that some parts of Zambia appear to exhibit naturally occurring iron. Tests are available to determine whether iron is naturally occurring or a result of corrosion, but there is no comprehensive map to indicate areas at risk of high levels of geogenic iron.
While stainless steel riser pipes have been used effectively, there are also some outstanding technical issues – particularly in relation to the removal of narrower diameter riser pipes, which require suitable tools that are not in the standard India Mark II toolkit. Further, the use of uPVC pipes has also been found to be problematic, as they need to be cut on removal and cannot easily be re-threaded. However, at least one NGO in Zambia has been using an alternative, comprising uPVC with stainless steel couplers which is available on the Zambian market. A further complication is that some parts of Zambia appear to exhibit naturally occurring iron. Tests are available to determine whether iron is naturally occurring or a result of corrosion, but there is no comprehensive map to indicate areas at risk of high levels of geogenic iron. Despite all of the efforts to date, and notwithstanding the widespread nature of rapid handpump corrosion of GI riser pipes and pump rods, the problem still persists in 2023.
Potential Next Steps for GRZ / International Donor Community / Universities
Revise the National Water Policy to include aggressive groundwater in community boreholes
Restrict Types of Handpumps to Certain Regions.
Enact a Law and a Statutory Instrument on Aggressive Groundwater in Community Boreholes.
Incentivise the private sector for provision of corrosion-resistant pipes and rods
Regulation of Quality of Handpumps by Zambia Bureau of Standards.
Standardise Handpumps Used in Zambia.
Further studies and replacement of galvanised iron riser pipes.
Further Research Studies on the phenomenon of naturally occurring iron in ground and surface water and
Research Studies on Saline Water in Western Province
You are invited to access the presentations HERE, along with the session’s concept and the study report: Nkhosi. J and Danert, K. (2023). ‘Stop the Rot: History of the Rapid Handpump Corrosion Problem in Zambia and Potential Next Steps. Action research on handpump component quality and corrosion in sub-Saharan Africa’. Ask for Water GmbH, Skat Foundation and RWSN, St Gallen, Switzerland. https://doi.org/10.13140/RG.2.2.27489.28006.
If you would like to dive deeper into the enriching exploration of water challenges and solutions through the Stop the Rot initiative, visit this page.
About the author:
Javan Nkhosi presenting at ZAWAFE 2023
Javan Nkhosi is a Zambian water professional. He has worked in the rural water sub-sector for more than 25 years on many water supply projects funded by the government, NGOs and donor agencies as a private consultant across Zambia. He has a passion for improving water supply to the unreached areas of rural Zambia. He holds a Diploma in Agricultural Engineering from NRDC, Lusaka, Advanced Diploma in Water Engineering from the Copperbelt University and an MSc in Project Management from the University of Lusaka. He is a Registered Engineer with Engineering Institute of Zambia (EIZ) and also a member of the Association of Consulting Engineers of Zambia (ACEZ) , an affiliate of the International Federation of Consulting Engineers (FIDIC).
References:
Danert, K. (2022) ‘Stop the Rot Report I: Handpump reliance, functionality and technical failure. Action research on handpump component quality and corrosion in sub-Saharan Africa’. Ask for Water GmbH, Skat Foundation and RWSN, St Gallen, Switzerland. https://doi.org/10.13140/RG.2.2.19733.81121
In 1983, I moved to live and work in Ghana – some 40 years ago now. Back then, I was the regional supervisor on the 3000 Well Maintenance Unit in Southern and Central Ghana which was funded by the German Development Service under the Rural Water Supply programme. The project was a pioneer of its time, and included drilling boreholes alongside the installation and testing of handpumps in six of Ghana’s regions, as well as the Nanumba district, Northern Region.
We initially installed India Mark II and Moyno pumps, before dropping the Moyno due to technical problems. However, we soon realised that the India Mark II pumps faced corrosion issues. Investigation and testing (as documented by Langennegger, 1989 and Langenegger, 1994) found that the Galvanised Iron components (rods and riser pipes), when installed in water with low pH, had a propensity to rapidly corrode – leading to discolouration of the water and affecting taste, but also causing the pumps to fail prematurely as the rods broke and riser pipes developed cracks and holes and even fell into the borehole. The envisaged idea of maintenance by communities, with assistance from mechanics who could reach villages by motorcycle, was simply not feasible with such installations. Another significant issue related to corrosion of hand pump parts was the water contamination and bad taste of the water. As a result, the water coloured the food and therefore caused the population to stop using the borehole water and forced them to go back to unsafe water sources
We, therefore, had to seek alternatives. This involved field testing and collaborating with the Materials Testing Institute of the University of Darmstadt.
We looked into replacing the galvanised iron components with stainless steel. To ensure the pipes were light, we considered using 3 – 3.5 mm thick pipes, and used a threading that at the time was used in the drilling industry , known as the “rope thread”. Although Atlas Copco had patented this threading type at the time, it was later manufactured in India after the Atlas Copco design period (patent) ended.
Figure 1: Rope thread (Claus Riexinger)
The pump rods presented some challenges as well, since the AISI Stainless Steel grade 316 that we were using was subject to breakage, including the threaded parts. In collaboration with our partners at the University of Darmstadt, we were able to find ways to make this grade of stainless steel more elastic by adding 2-3 % Molybdenum. Other issues with the rods related to the use of rolled thread, which we learned was more durable than cut thread. Incorporating these materials and techniques, we were able to reduce the rod diameter from 12 mm down to 10.8mm, resulting in lighter rods which did not corrode. The only drawback was that the threads could not be cut in the field, but this was not such an issue, as there was no need to cut them when they were installed, or upon maintenance.
Figure 2: Pump installation (Claus Riexinger)
After switching to stainless steel riser pipes, we encountered another issue: -galvanic corrosion between the pipe and the water tank. This type of corrosion occurs when two dissimilar materials come into contact in solution. It was yet another challenge! Fortunately, we were able to solve this problem by replacing the existing flange with a new one made of stainless steel with an insulating gasket, into which the riser pipe could be screwed and prevent any further galvanic corrosion.
Figure 3: Ghana Modified India Mark II Handpump – water tank, spout and flange
After conducting extensive testing and collaborating with the University of Darmstadt over a period of around 4 years, we managed to solve the problem of rapid corrosion of handpumps in Ghana. The improved pump design came to be known as the Ghana Modified India Mark II, and was officially adopted by the Government of Ghana in the 1990s. Its specifications can be downloaded here.
Designing and publishing the specifications for a new pump is one thing, but the other is ensuring that these are adhered to. A series of meetings with government, donors, and NGOs working in the water sector in the 1990s, led to the agreement to no longer use Galvanised Iron. All stakeholders were on board with the change.
Of particular importance was the tremendous support and buy-in of the major donor at the time – KfW (Germany). They agreed to pay for the increased costs of the Ghana Modified Pump on new installations, which at the time was about three times more expensive than the version using Galvanised Iron. KfW also supported the rehabilitation and replacement of the pumps that had previously been installed using Galvanised Iron. As a result, we were able to remove and replace the corroded installations systematically, rather than addressing the issue in a piecemeal manner.
It is estimated that over 4,500 Ghana Modified India Mark II handpumps had been installed in Ghana by the time I left the 3000 Well Maintenance Unit in 1992. Anecdotally, I would say that 90% were working, and of the 10% out of use, they were down for maintenance/repair.
KfW took this design to Cameroon, while Danida took it to Burkina Faso and Zambia. I am not fully aware of what happened next, but I do know that ensuring the quality of stainless steel was a problem in Burkina Faso.
I am very pleased to see that Ghana Modified India Mark II handpumps are now available through the Rural Water Supply Network (RWSN), and hope that these can be of use to other countries that are struggling to overcome the rapid handpump corrosion problem.
Figure 4: Example factory inspection Modified India MKII (Claus Riexinger)
However, I have a work of caution too. Although specifications, standards, and clear procurement documents are essential, they are rendered meaningless in the absence of inspection. During my time with the 3000 Well Maintenance Unit and later as an independent consultant, I traveled to India and other places for pre-shipment inspections. I also oversaw the rejection of consignments from India and Europe due to poor quality or manufacturing mistakes. And so, I urge all of you involved in handpump procurement and installation to make sure that you ensure the quality, especially through inspection and material testing.
About the author: Claus Riexinger is a rural WASH expert and freelance consultant with over forty years of experience in development cooperation with Government organisations, private companies, and development agencies mainly in Botswana, Lesotho, Malawi, Germany, India, Tanzania, and Ghana.
This year we are celebrating 30 years since the Rural Water Supply Network was formally founded. From very technical beginnings as a group of (mostly male) experts – the Handpump Technology Network – we have evolved to be a diverse and vibrant network of over 13,000 people and 100 organisations working on a wide range of topics. Along the way, we have earned a reputation for impartiality, and become a global convener in the rural water sector.
RWSN would not be what it is today without the contributions and tireless efforts of many our members, organisations and people. As part of RWSN’s 30th anniversary celebration, we are running a blog series on rwsn.blog, inviting our friends and experts in the sector to share their thoughts and experiences in the rural water sector.
This is a blog post from RWSN Member Hannah Ritchie, based in the United Kingdom
—
In 2020, I joined forces with Sand Dams Worldwide (SDW) to help them answer the question of “how long water from sand dams is lasting throughout the year”. In this short blog post, I am happy to discuss with you our findings and the implications of this study. We’ll be discussing “why we are interested in this question”, “how we researched this question”, and “what we found out”.
Firstly though, for those of you not familiar with what a sand dam is, I would like to direct you here for a video, which explains them better than I could, and here to SDW’s website where you can find everything sand dam related you might need to know.
Why are we interested (and why you should be too)?
So, why do we care about whether sand dams are providing water year-round? There is uncertainty over whether water from sand dams is lasting all the way through the dry season, or whether people can only abstract water from sand dams at the beginning of the dry season, when they have just been replenished by the rains. Because of this conflict in results, we can’t easily conclude how effective sand dams are as a dryland and specifically dry season water source. For example, can people rely on them when other water sources are unavailable (such as when surface waters have run dry)? Or are the dams dry by the second week of the dry season? Answering this question is very important for understanding their level of use, acceptance, and financial viability, helping to inform future water management interventions and to ensure that communities are serviced with a continuous improved supply. Knowing whether there are certain dry season months when sand dams have no water being abstracted can also inform on months when water supply from other sources needs expanding. Finally, knowing which sand dams have more or less water being abstracted can aid in optimising sand dam design.
You might be thinking, “but no water abstracted doesn’t necessarily mean no water being available”, and you would be right. Because, whilst abstraction volumes may be linked to storage, many other variables, such as convenience, quality, and the use of other sources can also impact abstraction. Thus, the contribution that sand dams make to water security is not synonymous with the amount of water actually stored in the dam. Therefore, whilst this study can show us abstraction patterns from sand dams and therefore behaviours of use, it cannot confirm for certain whether there is or isn’t any water available.
How did we do it?
Now you know why we’re interested and why it matters, how did we actually go about answering the question: “how long water from sand dams is lasting throughout the year”? In 2019, 26 sand dam hand pumps in Makueni and Machakos Counties, Kenya were fitted with Waterpoint Data Transmitters (WDT) by ASDF. These devices measure the number of times and with what force a handpump is used over an hour and convert this into an estimated volume of water abstracted (Thomson et al., 2012). This data point is then transmitted by SMS. I had access to this remotely sensed data from April 2019 until October 2021. With a data point every hour for 26 sites over 31 months, I ended up with a very large data set!
Alongside this abstraction data, I also had access to interview and observation data provided by MSc student Joanna Chan, ASDF, and SDW. These variables included perceived salinity, abstraction limits, livestock use, whether the dam is said to have ever run dry, presence of rainwater harvesting tanks, actual salinity (μs/cm), area of dam wall (m2), average distance travelled from home to dam (km), and user numbers (Chan, 2019).
This data was then analysed to assess how much water people were abstracting and for how long throughout the year the water continued to be abstracted for. The variables collected from interview and observation were then analysed to provide insight into differences in abstraction between sites. For example, did sites with larger dam walls have more water being abstracted, or did salinity impact abstraction in any way?
Finally, we looked specifically at the last week in September (as a proxy for the end of the long dry season) to assess whether enough water to specifically meet drinking water needs (2 L/p/day) was still being abstracted at any sites. Due to the necessity of an improved source of water for drinking (of which a handpump is one), we wanted to know whether the handpumps could independently meet drinking water needs, in case no other water sources were available.
What did we find out?
After analysing all of the data and wrapping my head around some statistical analysis, I like to think that we found some interesting results.
The most obvious finding was that of high variability in abstraction volume between the 26 hand pumps and seasons. We found abstraction to be significantly higher in the long dry season, indicating a high reliance and delivery of water when other sources are compromised. The diagram below shows median monthly abstraction (L/month) (red line) and average monthly rainfall (mm) (brown bars – dry season and blue bars rainy season) across all sites – indicating higher abstraction when rainfall is lower.
There was abstraction data available from 21 handpumps (81%) by the end of at least one of the analysed long dry seasons, with at least some water still being abstracted. At 59.1% of these sites, enough water to meet each user’s drinking water needs (2 L/p/day) was being abstracted in at least one of the analysed years. This indicates that such dams can meet the drinking water needs of users independently of other sources.
Using the variables which were collected in interviews and observations, we found that sites with a greater proportion of people using the water for livestock, higher salinity, and larger dam walls had significantly higher levels of abstraction. This is to be expected as higher salinity sites are often used more for livestock (Chan, 2019), which have a greater water demand than that for drinking, whilst larger dam walls can lead to a greater volume of sand build up and therefore water storage (Maddrell & Neal, 2012).
These results highlight sand dams as a sustainable alternative to other dry season sources such as water vendors, which can be expensive and unreliable. However, lower abstraction in certain months and sites highlights that we must approach water management holistically. No one technique is necessarily the answer to dryland water security and all available water sources must be considered. Clearly, not all sand dams behave the same, with certain sand dams always likely to have higher levels of abstraction than others. However, high abstraction and sustained water availability by the end of the long dry season at many sites profess the positive contribution that sand dams can make to a community’s water supply, offering opportunities for further success in the future.
Closing remarks
I really hope you enjoyed learning about abstraction trends from sand dams as much as I enjoyed studying them (most of the time!) If you’re interested in learning more, I hope the paper will be published soon, which will be freely available for everyone to read. If you’d like to reach out, my email is hannah.ritchie@cranfield.ac.uk. Many thanks for reading.
A bit about the author
I am a PhD student at Cranfield University. I began my PhD in September 2019 in WaSH with the CDT Water WISER. With a background in geology and environmental engineering, I wanted to design my PhD project around earth sciences and development. This was how I ended up finding sand dams and partnering with SDW and Africa Sand Dam Foundation (ASDF).
Outside of work I love to run, hike (generally be outdoors as much as possible), read, and am learning French. I am very passionate about science communication and firmly believe that research results need to be translated into accessible formats for all to read and understand, hence why I have written this blog post for you (definitely shorter, more fun, and less boring than reading a 15-page paper!)
Did you enjoy this blog? Would you like to share your perspective on the rural water sector or your story as a rural water professional? We are inviting all RWSN Members to contribute to this 30th anniversary blog series. The best blogs will be selected for publication. Please see the blog guidelines here and contact us (ruralwater[at]skat.ch) for more information. You are also welcome to support RWSN’s work through our online donation facility. Thank you for your support.
Photo credits: Hannah Ritchie
References
Chan, J. (2019). Abstraction of Water from Sand Dams in Machakos and Makueni Counties (Kenya) via Handpumps.
Maddrell, S., & Neal, I. (2012). Sand Dams: a Practical Guide.
Thomson, P., Hope, R., & Foster, T. (2012). GSM-enabled remote monitoring of rural handpumps: A proof-of-concept study. Journal of Hydroinformatics, 14(4), 829–839. https://doi.org/10.2166/hydro.2012.183
Este año celebramos los 30 años de la fundación formal de la Red de Abastecimiento de Agua en Zonas Rurales. Desde unos inicios muy técnicos como grupo de expertos (en su mayoría hombres) la Red de Tecnología de Bombas de Mano- hemos evolucionado hasta convertirnos en una red diversa y vibrante de más de 13.000 personas y 100 organizaciones que trabajan en una amplia gama de temas. En el camino, hemos ganado una reputación de imparcialidad, y nos hemos convertido en un convocante global en el sector del agua rural.
La RWSN no sería lo que es hoy sin las contribuciones y los incansables esfuerzos de muchos de nuestros miembros, organizaciones y personas. Como parte de la celebración del 30º aniversario de la RWSN, estamos llevando a cabo una serie de blogs en rwsn.blog, invitando a nuestros amigos y expertos del sector a compartir sus pensamientos y experiencias en el sector del agua rural.
Este blog fue escrito por nuestro miembro de RWSN, Jaime Aguirre, de Bilbao, España.
EMAS es el acrónimo de “Escuela móvil del agua y saneamiento”; fue acuñado en los años 80 en Bolivia por Wolfgang Buchner, con el apoyo de un grupo de voluntarios
La misión principal de EMAS es enseñar a las familias a obtener agua limpia por sí mismas. El “aprendizaje práctico” es la forma más óptima de aprender estas técnicas.
El programa WaSH de EMAS incluye varias tecnologías Do-It-Yourself, como la bomba manual EMAS, la perforación manual de pozos de hasta 90 metros, tanques de almacenamiento de agua y los aseos VIP, entre otros. Todas las tecnologías han estado en constante desarrollo desde los años 90. Se han implantado en más de 25 países, principalmente en América Latina y África. La biblioteca de la RWSN alberga documentación y evaluaciones del uso de las tecnologías EMAS en Uganda, Sierra Leona, Panama y Bolivia, entre otros.
El objetivo de las tecnologías de EMAS es facilitar el acceso al agua potable y al saneamiento mediante la formación de técnicos locales y beneficiarios. Estas formaciones son cursos compactos en los que durante varias semanas se muestran y practican todas las técnicas. A largo plazo, todas las instalaciones pueden ser mantenidas por el usuario debido a la simplicidad de la tecnología. El resultado:
Mejora del acceso al agua potable para las poblaciones rurales del mundo, combinada con instalaciones sanitarias sencillas, evitando así la propagación de enfermedades infecciosas y reduciendo las tasas de mortalidad.
Aumento de la calidad de vida, por ejemplo, al eliminar el laborioso acarreo de agua, lo que ahorra tiempo a las mujeres y los niños y permite realizar pequeños trabajos agrícolas.
Los constructores de pozos formados son autosuficientes e independientes, y pueden, si es necesario, recibir más asesoramiento y formación.
Sostenibilidad: Los pozos y las instalaciones de agua son muy asequibles. La experiencia ha demostrado que los propietarios mantienen bastante bien las instalaciones, lo que se traduce en una larga vida útil. Las reparaciones que puedan ser necesarias suelen ser fáciles de realizar.
Todos los materiales necesarios para estas reparaciones pueden obtenerse localmente.
Los materiales y los métodos son respetuosos con el medio ambiente y la mayoría de los pasos se realizan manualmente.
La extracción de cantidades moderadas de agua y su uso disciplinado no tienen un impacto negativo en el medio ambiente ni en los niveles de agua subterránea.
Mejora de las oportunidades para que las personas permanezcan en sus regiones de origen de forma permanente.
La bomba manual EMAS es el componente clave de las tecnologías EMAS porque es capaz de bombear agua verticalmente hasta 50 m. Mientras que otras bombas manuales tienen una mayor resistencia al uso intensivo o incluso inapropiado (muchas veces cuando la bomba está siendo utilizada por toda una comunidad), la bomba EMAS está diseñada principalmente para el uso doméstico. Las bombas EMAS tienen una larga vida útil, ya que las reparaciones que puedan ser necesarias suelen ser fáciles de realizar por el usuario.
Las instrucciones en vídeo pueden verse en nuestro canal de YouTube que cuenta con unos 15.000 seguidores y algunos vídeos tienen más de 700.000 visitas.
A veces hay que hacer adaptaciones de las tecnologías en algunos países debido a la disponibilidad de material.
Amadou, técnico de Senegal marchando con su equipo de perforación a hacer un nuevo pozo
Por el momento, se han perforado aproximadamente 70.000 pozos EMAS en todo el mundo. La mayoría han sido financiados por las familias o los beneficiarios. Desde los años 80, más de 100 técnicos formados han creado una microempresa que ofrece servicios WASH a su comunidad. Las tecnologías de EMAS se han implantado en más de 25 países a través de cooperaciones con diversas organizaciones locales e internacionales (por ejemplo, OPS). Como resultado de la cooperación con Welthungerhilfe se han perforado más de 3.000 pozos EMAS en Sierra Leona.
EMAS pretende asociarse con organizaciones que incluyan WASH en sus programas y que también deseen implementar las tecnologías mencionadas a través de proyectos de formación en WASH. Los proyectos deben incluir un seguimiento y apoyo a los técnicos WASH formados durante su camino para convertirse en PYMES. Muchos casos demuestran que los trabajadores de las PYMES crean su propia empresa y sirven a otras regiones que tienen una gran demanda de servicios WASH.
A corto plazo, se lanzará una página de aprendizaje de EMAS para compartir todas las experiencias en varios países y también facilitar todo el material disponible. Esta página también se dirigirá a los usuarios con conocimientos técnicos que deseen aprender más sobre las tecnologías.
Curso de creación de bombas EMAS en Sierra Leona
Perforación en Mali
Sistemas EMAS incluyendo captación de agua pluvial con cisterna enterrada, bomba manual, ducha, lavamanos y baño
Sobre el autor: Jaime Aguirre es originalmente un ingeniero mecánico que trabajo muchos años como ingeniero de diseño en el sector de la energía eólica. Después de algunas experiencias decepcionantes con la implementación de tecnologías WaSH de alta tecnología, se unió en 2014 voluntariamente a una formación EMAS en Bolivia. Desde entonces, se ha dedicado permanentemente a impartir formación junto con la ONG EMAS-International e.V. con sede en Alemania. En 2015 puso en marcha la ONG española TADEH en Bilbao, España, que ofrece formación en tecnologías de autoabastecimiento EMAS en todo el mundo.
¿Le ha gustado este blog? ¿Le gustaría compartir su perspectiva sobre el sector del agua rural o su historia como profesional del agua rural? Invitamos a todos los miembros de la RWSN a contribuir a esta serie de blogs del 30º aniversario. Los mejores blogs serán seleccionados para su publicación y traducción. Por favor, consulte las directrices del blog aquí y póngase en contacto con nosotros (ruralwater[at]skat.ch) para obtener más información.Si aprecia el trabajo de la RWSN y desea apoyarnos económicamente, puede hacerlo aquí.
This year we are celebrating 30 years since the Rural Water Supply Network was formally founded. From very technical beginnings as a group of (mostly male) experts – the Handpump Technology Network- we have evolved to be a diverse and vibrant network of over 13,000 people and 100 organisations working on a wide range of topics. Along the way, we have earned a reputation for impartiality, and become a global convener in the rural water sector.
RWSN would not be what it is today without the contributions and tireless efforts of many our members, organisations and people. As part of RWSN’s 30th anniversary celebration, we are running a blog series on rwsn.blog, inviting our friends and experts in the sector to share their thoughts and experiences in the rural water sector.
This is a guest blog by RWSN Member Jaime Aguirre, based in Bilbao, Spain.
EMAS is the Spanish acronym for “Escuela móvil del agua y saneamiento” meaning Mobile School of Water and Sanitation; the acronym was coined in the 1980´s in Bolivia by Wolfgang Buchner, supported by a group of volunteers.
The main mission of EMAS is to teach families how to obtain clean water by themselves. “Hand-on learning” is the most optimal way to learn these techniques.
The EMAS WaSH scheme include various Do-It-Yourself technologies like the EMAS manual pump, manual well drilling up to 90 metres, water storage tanks, and VIP toilets among others. All technologies have been in constant development since the 1990’s. They have been implemented in more than 25 countries, mostly in Latin America and Africa. The RWSN library hosts documentation and assessments of the use of EMAS technologies in Uganda, Sierra Leone, Panama and Bolivia amongst others.
The goal of EMAS technologies is to provide access to clean water and sanitation through training of local technicians and beneficiaries. These trainings are compact courses where over several weeks all techniques are demonstrated and practiced. In a long term, all facilities can be maintained by the user due to the technology’s simplicity. The result:
Improved access to clean drinking water for the world’s rural populations combined with simple sanitary facilities, thus preventing the spread of infectious diseases and reducing mortality rates.
Increased quality of life, e.g. by eliminating laborious water-hauling, thus saving women and children time and enabling small farming operations.
The trained well builders are self-sufficient and independent, and can, if necessary, receive repeated advising and training.
Sustainability: The wells and water facilities are very affordable. Experience has shown that the owners maintain the facilities quite well, which results in long service lives. Any repairs that may be needed are usually easy to complete.
All materials needed for these repairs can be obtained locally.
The materials and methods are environmentally responsible and most of the steps are performed manually.
The withdrawal of moderate amounts of water and its disciplined use have no negative impact on the environment or groundwater levels.
Improved opportunities for people to stay in their home regions permanently.
The EMAS hand pump is the key component of the EMAS-technologies because it is capable of pumping water vertically up to 50 m. While other hand pumps have higher resistance to intensive or even inappropriate use (many times when the pump is being used by a whole community), the EMAS pump is designed mainly for household use. EMAS pumps have a long service life since any repairs that may be needed are usually easy to complete by the user.
Video-instructions can be viewed on a YouTube channel which counts about 15.000 followers with some videos having over 700.000 views.
Sometimes adaptions of the technologies have to be made or are even necessary in some countries due to material availability.
As of now, approximately 70.000 EMAS wells have been drilled worldwide. The majority have been financed by the families or beneficiaries. Since the 1980’s, worldwide more than 100 trained technicians have created a micro enterprise offering WASH services to their community. EMAS technologies have been implemented in over 25 countries through cooperations with various local and international organizations (e.g. PAHO (Pan American Health Organization) ). As a result of the cooperation with Welthungerhilfe more than 3.000 EMAS wells have been drilled in Sierra Leone.
EMAS aims to partner with organizations which include WASH in their programmes and also wish to implement the mentioned technologies trough training projects in WASH. Projects should include follow-up and support to trained WASH technicians to help them in becoming SMEs. Many cases show that workers of SMEs create their own company and serve other regions which have high demand for WASH services.
An EMAS learning page will be launched shortly in order to share all experiences in various countries and also facilitate all available material. This webpage will also target users with technical skills who wish to learn more about the technologies.
Drilling a well in Sierra Leona WASH Center
Amadou, EMAS technician from Senegal going with his drilling equipment to make a new well
Training of EMAS pump making at Sierra Leone
Drilling training at Mali
EMAS systems including rainharvesting, underground tank, bomba manual, toilet, shower and sink
About the Author: Jaime Aguirre is originally a mechanical engineer who acted many years as design engineer in the wind energy sector. After some disappointing experiences with the implementation of high-tech WaSH technologies he joined in 2014 voluntarily an EMAS training in Bolivia. Since then, he has permanently been engaged in providing training together with German based NGO EMAS-International e.V. In 2015 he initiated the Spanish NGO TADEH in Bilbao, Spain which provides training in EMAS Self Supply technologies worldwide.
Did you enjoy this blog? Would you like to share your perspective on the rural water sector or your story as a rural water professional? We are inviting all RWSN Members to contribute to this 30th anniversary blog series. The best blogs will be selected for publication. Please see the blog guidelines here and contact us (ruralwater[at]skat.ch) for more information. You are also welcome to support RWSN’s work through our online donation facility. Thank you for your support.
Rural Water Supply Network - blog 