This page is about earth dam construction for water retention purposes. Building a small to medium-scale earth dam like the ones described on this page can provide water for irrigation, aquaculture, recreation, ecosystem restoration, and other uses.
Note: We are not experts in earth dam design. We’ve just done an immense amount of research on the topic after identifying a need for earth dams as part of the open source One Community Highest Good Housing and Food components.
We share all we’ve learned with the following sections:
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Earth dam construction is a viable option in many places for water storage and pond or lake creation. Systems will vary from place to place, so the design of your water storage feature warrants flexibility and careful observation of the surrounding landscape. The ideal solution is one that maximizes water storage and minimizes human intervention. This can be accomplished by mindfully educating ourselves on the natural elements we are working with.
The earth dam construction content here is from hours of research on this topic. Our goal is to organize what we’ve learned into some broad guidelines and hopefully turn a nebulous and daunting task into a viable water-retention solution. The overall steps of the process are outlined in the flowchart below.
Dams encircle the lower perimeter of where water wants to flow to create ponds that are replenished by both surface runoff and subsurface flow. Although water tanks are preferred for drinking water, they can cost 100x more for the same amount of water stored in an earth dam. The ponds and lakes created by small earth dams also develop valuable wetland ecosystems, beautiful recreation areas, aquaculture options, and large-scale water storage for emergency and/or agricultural use. Small DIY earth dams minimize flooding during the wet season, keep water from drying up during the dry season, combat erosion, and allow the standing water behind the earth dam to better percolate into the ground, recharging the groundwater and raising the water table. In addition, small DIY earth dams also lend the possibility of serving as small scale electricity generation for supplemental power needs through properly planned mini and micro-scale hydro power options.
Tamera Eco-Settlement Water Conservation Results: This Took Less Than 4 years
Our goal with this page is to share everything our research has taught us about DIY earth dam construction. There are many different types of earth dams that you can construct, but the basics of construction are the same. The image below shows the most common earth dams and we use the following sections to discuss each of these (and others) and the ways to build them:
You must be aware of and adhere to local laws before constructing an earth dam. Failure to do this can lead to forced removal of your construction. Plan ahead for this because meeting with the local watermaster, local county authority for land use permitting, fish and wildlife services, and/or the state for permission can take 6 months or more
Depending on the size and location of your earth dam, you may also need to enroll a civil and/or structural engineer in the design process. Here are a few of the things to think about:
These and any other safety concerns need to be thought of and addressed from the beginning.
Constructing an earth dam without proper safety measures can result in structural failures, landslides, or ecological damage. Engaging engineers and addressing site-specific risks ensures the dam’s stability and the safety of surrounding areas, preventing catastrophic failures.
It’s a scary business, it’s scary designing, especially when a lot of dirt’s been moved and sheets of water are spreading across the landscape. That’s scary. And if it scares you too much, get someone in to do it.
~ Bill Mollison ~
Typically, 1.6 to 3 feet (0.5 to 1.0 meter) of clay is needed to seal an earth dam. The pond water level naturally fluctuates, resulting in periodic wetting and drying of the pond bed. When the bed is exposed and not submerged under water, the clay layer can crack as it dries and these cracks can go down about 1.6 feet (0.5 meters), so 3 feet (1 meter) is ideal to account for this natural cyclical process.
When enough clay is not available at the site of the pond, we must consider other alternatives to seal the pond bed. The benefits of having a pond for water storage outweighs the use of non-natural materials that may be needed. If a pond is leaking, these methods can be tried – ideally in this order if the goal is minimum effort:
There are many different types of earth dams you can construct. This table shows the most common types.
Here are all the good locations we could find for each of the above using a topo map, Google Earth, and 1-square-mile parcel of land.
Note: The Photoshop topo overlay in this image is not as accurate as the Sketchup overlays above and below.
We explore each of these (and a few others) with additional notes and more specific imagery below.
Valley earth dams are constructed across a valley or gully. These dams, sometimes called a “barrier dam,” are most frequently used as energy systems. Especially when built in the path of a flowing or intermittent stream bed. These dams are also valuable for storing large volumes of water, as well as for irrigation. For these dams, it is particularly important to overdesign the spillway and accommodate any fish passage that has been obstructed due to dam installation.
Ridgepoint earth dams are located on flattened portions of descending ridges and are quite rare. It is composed of a single, horseshoe-shaped wall. These dams are most useful for water storage and runoff collection.
Keypoint earth dams are located in lower countries where hills transition from convex to concave. These dams are primarily used to store irrigation water and are amenable to being placed in series on descending contours. These are most appropriate for 4-12% slopes.
Contour earth dams are located along hillsides where the contour widens on relatively flat terrain (slope of 8 percent or less). They are 3-sided and the front of the dam is either concave or convex to follow the contour. They are most useful for domestic livestock and aquaculture. These tend to be relatively expensive in comparison to their water storage capacity. Like keypoint dams, contour dams are amenable to being placed in series on descending contours. There is insufficient natural catchment so diversion channels or swales are essential.
Turkey nest earth dams are earthen water storage tanks best placed on the highest available site with flat ground. These dams do not capture runoff, so they must be filled with external water sources. These are much cheaper than constructed tanks, but limited to use for irrigation, whereas constructed tanks can be used for drinking water as well. These dams should be at least 100 feet x 100 feet x 10 feet (providing approximately 0.6 million gallons of storage) to be cost effective.
Saddle earth dams are unusual because this type of land feature is rare – a saddle between two hills. These dams have two walls. These dams are most useful for fire control and ecosystem/wildlife support. This type of dam typically ends up being the highest dam on the landscape and has the potential to fill from hill runoff.
A barrage earth dam is one of the least likely DIY dams you’d probably consider constructing. This is because they incorporate a large mechanical component to control gates that regulate the amount of water they store. Barrage dams are normally built near the mouth of the river and used to divert water for irrigation needs or limit the amount of water going down-stream. Water builds up behind these dams and a number of large gates are opened or closed to control the amount of water passing through. This allows the structure to regulate down-stream water while also stabilizing river water elevation upstream for use in irrigation and other systems.
Here’s a video about these commonly commercial-scale dams. It provides a good explanation of the difference in function between a traditional dam and a barrage dam.
Here we discuss the steps for constructing your own earth dam. Again, we’re not experts in earth dam design or construction. We’ve just done an immense amount of research on the topic after identifying a need for earth dams as part of the open source One Community Highest Good Housing and Food components. We share here all we’ve learned with the following sections:
Throughout the life of the project, engage in a dynamic thinking process and be flexible and receptive, allowing nature to be your guide. During the planning stage it is important to clearly define the purpose and overall desired outcomes of the project and identify the resources available. Include in your resource evaluation your financial resources, your equipment resources, the lay of the land, and personal and local knowledge base.
Earth dam construction involves significant risks, including structural failure, environmental damage, and legal issues. Engaging engineers and complying with local regulations is essential to mitigate these risks, ensuring the project’s safety and sustainability while protecting downstream communities.
When working with nature, it is imperative to have a variety of applications that serve the same or similar end uses. With a water retention landscape, it is wise to have a mixture of earth dam types to meet your end-use needs. This is safer and usually easier. It also better prepares you for unpredictable natural events, such as seasonal and intraseasonal extreme weather variations. To select the appropriate number and types of earth dams, the following table can be utilized:
Here are some additional guidelines:
It is crucial to have soil with sufficient clay content for the earth dam structure, as well as the pond bottom. Soil with at least 40 percent clay is necessary to build a water-tight earth dam, and to retain water in the pond. Given the importance of this criteria, it is worth the money to rent an excavator to dig and evaluate the soil at the potential earth dam sites identified in the step above. The “Taking Test Slices” section below discusses how to do this.
Use models and small experiments to more deeply understand the local landscape’s potential for water storage. It is very hard to work with free-draining soil (deep or coarse sands), rocky areas, and/or areas too steep or unstable. The bottom of gentle slopes are usually better choices.
If clay has to be brought in (versus mined on your own property), rethink the pond location and/or water storage method.
Taking test slices helps you understand the types of soil you will be dealing with. Using an excavator (if available), assess the geology 6 to 12 feet below the ground surface at around 6 different locations. You can go as deep as 15 feet, but beyond that returns diminish. Dig until an impermeable layer is reached near the depth you want your pond to be. This article called “soil permeability” explains well what you are looking for and why.
The geology can be significantly different just 30 feet away. In some areas it is helpful to have the excavator put each scoop in sequence so each layer can be assessed for clay content. The excavated materials (called the “overburden”) may need to be sorted to arrive at the correct clay content. Forty percent clay or more is the goal. If you don’t have 40 percent or more clay, another area on the property may need to be mined. The video below shows how to test and measure your clay content.
Note: For earth dam construction, it is preferable to use test slices over coring. This is because coring typically only provides an assessment for the first 3 feet below the ground surface and you are seeking to assess your soil between the depths of 6 and 15 feet.
Earth dams may not be the ideal solution for all locations and there are many different kinds of earth dams (see “Types Of Dams” above). Here are the key guidelines our research identified:
Sepp Holzer uses a water-retention-landscape style where the surrounding forest is your water reservoir. Water from your dammed area spreads through the surrounding ground and helps develop a lush landscape. The picture and video below are about one of Sepp’s earth dams and the landscape like this that he created.
Tamera Eco-Settlement Water Conservation Results: This Took Less Than 4 years
A successful water retention landscape can be created using basic principles and well-established parameters. At a minimum, a water retention landscape consists of earth dams, embankment ponds, spillways, and erosion control interventions. On some landscapes, sediment traps, diversion drains, and swales make sense. In simple terms, assure that the local soil has at least 40 percent clay, all earth dam walls can be less than 20 feet (6 meters) high and still meet minimum volume/end-use requirements, and that the pond length behind the earth dam is at least 3 times longer than that earth dam’s length. An expanded array of details is provided in the image and text below:
Below are our notes taken regarding the main features shown in the image above:
“Wherever you are doing earthworks, you need to carefully remove the topsoil and not conglomerate topsoils and subsoils together. It’s taken 100s or 1000s of years to make that topsoil, you’re not going to make it again too easy. Separate it and then make your shapes and forms.”
~ Geoff Lawton ~
For desert landscapes, have your silt (or sediment) trap above the main water feature.
You can put in other attachments too. Examples are swales (tree-growing systems), ledges for plants, and/or deep-water refuge for fish in areas where water freezes.
Wherever you are in the business of making swales, work out how big they ought to be, then triple it. If they’re going to be a meter wide and a meter deep, make them 3 meters – 4 meters wide, and 3 meters deep and you might hold those big events. But if you don’t, it’ll blow the lot out. If your top swale blows, then the bank goes, and all your other swales go.
~ Bill Mollison ~
Two case studies are presented below from work completed by Geoff Lawton. These are from the Permaculture Design Course DVDs where he taught with Bill Mollison. One key takeaway from both is placing emphasis on making things very level, so water flows will soak passively and carry nutrients around the property. We’ll add our own case studies here with videos, much clearer explanations, and complete tutorials as we complete our own dam constructions as part of the 7 sustainable villages.
The first case study presented is Lawton’s permaculture property that he eventually sold to one of his students. The property is located North of Brisbane, Australia on the sunshine coast where it rains quite a bit. The property is 5 acres and zoned as a small farm, about half forested and half farm fields. The forested area was inaccessible because of a valley with a creek running through it. There are three creeks on the property:
Lawton completed the work successionally – taking approximately ½ of his time for 2 years. An image of the work (dams, swales, and roads) is shown in the screen capture below from the video where he discusses this case study:
DIY Dam Case Study – Geoff Lawton’s Brisbane, Australia Property
The first thing Geoff did was install a dam to gain access to the forested side of the property that was originally deemed unusable – the road over the dam is what allowed access. A serious 8-meter wide spillway was also installed that fed back into the primary stream. It was big to minimize the erosion potential to the dam wall. During big rains, 1 meter of water would go over the spillway. A pump was installed with a float and weighted foot valve to transfer water to the top of the property. The inlet to the pump was held below the water surface with a weight and off the floor of the dam with a float. The next two were placed in succession on the secondary creek with the spillway of the upstream dam feeding into the dam in series and the second dam fed into the third stream that originated on the property. Lawton believes that replacing 20-year-old growth forest with bodies of water is beneficial because life is boosted by increased water retention.
When a wet spot was noticed at the top of the property, a contour dam (also called a top tank) was installed. It was supplied partially by the road and nature strip. Its spillway drained into multiple swales on-contour that were in-series to direct the water around the farm field. This contour dam had geese and ducks, which resulted in nutrient-rich water. When water is released during the dry season, it takes a couple of days to soak into the dry ground, then it only takes a few hours to soak the land with nutrient rich water.
Then in the bottom corner of the property, it started to get boggy after about 6 months. A neighbor began complaining about this effect, so Lawton dug a trench 2 meters wide, 1 meter deep and put the excavated material on the downhill side. When earth movers hit clay in the trench, they compacted it by hitting it with the back of the bucket. This half circle pond filled quickly. After this, a third large swale was added to further disperse the water throughout the property. Lawton hand-dug 8 to 10 meters every day for about a month and the swale ended up being more accurate than the excavator.
The neighbor continued to submit complaints and caught Lawton on a technicality, which led Lawton to improve upon his design even further. Lawton was not allowed to divert any flow from the secondary stream to the third stream. This led to the addition of another contour dam on the third creek that was connected to the dam on the secondary stream using a canal (angled banks going down to a flat bottom). Two spots were picked that were the same elevation to have easy control over the direction of the water flow. The lower dam wall was extended to cover both the secondary and third creek, which created yet another pond at the third stream. Mounds and swales were used to direct extra water into the third creek and with a slight height difference and sluice gate to direct water back to the secondary stream, so no water was being diverted from there.
Beyond this work, Lawton also had small swales near the simple temporary home near the gardened (bamboo and legumes) area for kitchen flows. These swales were 2 meters across, 1 meter deep and with 2 meters across and 1-meter high mounds. Graveled footpaths were also added between the gardens off the lower-corner dug pond, where water had been pooling near the neighbor’s property. Because the footpaths were next to the pond, they were partially flooded with water. He trellised over the pond and grew trees on the mound next to the pond and used water weeds as mulch for the garden. The last addition was a ridge point dam, which was the 7th body of water added to the property. Lawton essentially confused the catchment, melded them together and while he fixed one problem, he technically caused another problem, but creatively fixed that too. In the end, Lawton achieved the goal of having 15% of the property under water.
The second case study was a consulting project that Lawton worked on located in Clunes, Northern Wales. It was a hilly project serving as a demonstration and teaching site. The work completed included building two dams, a large lower valley dam and a small upper contour dam.
The entire process began with a plan on a good contour map. In the lower one, a mix of bad soil and clay were found, so earth workers and their machines had to find better material elsewhere on the property, as well as blend dirt together to attain the appropriate clay-content necessary for the keyway and water-side of the dam wall. This was especially important to do because the lower dam had a decent flow and catchment area to it. Valley dams, like this one, are important to seal.
The lower dam was built with a Jetty too. Jetties have to be pre-built before the dam is filled with water. These provide a clean edge to the dam and somewhere peaceful to sit. The top of the dam was also a minimum of 3.5 meters wide so tractors and other average-sized machines could go across it to trim growth or do other work. Topsoil was placed (it is like icing a cake) on the waterline and then hydro mulched with seed (i.e. sprayed with wet mulch containing seed). The hydro mulch contained pioneer trees, bushes, and cover crops, along with organic glue and shredded paper.
The lower large dam used a large spillway swale with level sills and was installed by ripping the soil with a tilted blade on contour. All heights were checked with a laser level (laser level emitter on tripod and laser receiver – earth movers sometimes have these for rent) and considered adequate when within 10 mm. The elevations were marked before starting and double checked along the way and at completion. To achieve clear water (the clarity of a dam at best is usually weak tea type of clarity), he installed three silt trap ponds before the dam and made sure the edges were well vegetated.
This second dam was installed 20 meters above the house and acted as their water tank. A dam holding about 125,000 gallons is less than half the price of a tank holding that same volume. It is more economical to build a key point dam on top of the property.
Notable comment from this case study: It can be surprising what you find when you start digging. You never quite know what you are going to hit. If you hit a big rock and you don’t know how big it is, have the bulldozer bump/ram (as hard as he can) the rock while you stand next to the rock. If the ground shakes, then it is a floater, meaning it has a bottom and you can typically move the rock out of the way or work around it. If there is no shake, the rock is part of mother earth. Earth moving contracts usually mention OTR, which stands for Other Than Rock, because rocks are hard to deal with and hard on the machines.
Conducting a thorough cost analysis is essential to assess the financial feasibility of a dam project. The methodology for estimating costs and the expected range of accuracy will vary depending on the project’s stage of development and intended use. For projects at different maturity levels—such as conceptual, preliminary, or detailed design phases—specific estimation techniques are applied, each offering varying degrees of precision. One of the most commonly used methods in engineering projects is unit cost estimation, which assigns a cost per unit of work (e.g., per cubic meter of clay materials). As the project becomes more defined and detailed, the estimate evolves to include more precise line items, often at the assembly level, along with take-off quantities for greater accuracy.
However, several factors can introduce biases or uncertainties into cost estimates, including the quality of reference data, assumptions about key variables, market conditions, construction timelines, and the estimator’s experience and expertise. Therefore, a careful and critical evaluation of these factors is required to minimize estimation errors and ensure the project’s financial viability is accurately assessed.
The Manual on Small Earth Dams provides a table detailing various items essential for conducting a cost analysis. With the preliminary dam construction design in hand, users can utilize this table to assess expenses effectively. The items are categorized as follows: the first three belong to the preliminary and design phase. This phase includes expenses such as permits, land acquisition, and other necessities required to proceed with construction. The following items are classified as direct construction costs, reflecting expenses directly associated with the physical construction of the dam. It’s important to note that additional items may be included based on the specific circumstances of the project.
At the bottom of the table, the “contingencies” box, which requires entering a percentage, serves to provide a financial buffer against uncertainty. The contingency amount can be determined using methods such as range estimating, as introduced by the Association for the Advancement of Cost Engineering (AACE).
The report provides high-level (low accuracy) cost estimates for various dam storage configurations within the Hughenden Irrigation Project, facilitating the evaluation of infrastructure needs against changes in dam yield to identify optimal storage solutions. In the cost section, alongside previously mentioned items, key factors such as miscellaneous costs, general expenses, contractor profit, and taxes are also discussed. Given the limited available information, costs are estimated based on certain assumptions, such as calculating them as a percentage of direct costs. This approach is common in the early stages of planning and design, though it may lead to unavoidable inaccuracies.
For typical dam designs, online resources, such as reports from the Norwegian Water Resources and Energy Directorate (NVE), provide a cost curve that estimates the costs associated with small rock-fill dams and three types of concrete dams. This cost curve facilitates easy estimation based on dam height and length. The cost curve is derived from specific unit prices and accounts for 20% in preparing and running costs. However, it is important to note that the cost curve is based on certain assumptions, was developed several years ago, and reflects conditions specific to Norway. As such, it may not accurately represent current situations in your project area. Therefore, while it can serve as a rough estimate, a detailed cost estimation is still necessary for your specific site and design.
Cost analysis in dam construction is complex and subject to numerous site-specific and external factors. Several key factors need to be carefully considered, particularly because the nature of dam construction is heavily reliant on civil engineering work, which varies significantly depending on site conditions. For example, remote sites tend to incur higher transportation costs due to the challenge of delivering materials, equipment, and labor over longer distances. Additionally, sites with complex geological conditions lead to increased construction challenges, raising the overall costs due to the complexity of the engineering work.
Research on dam costs and overruns shows that cost overruns are more significant compared to other construction projects. A key factor identified is the length of the construction period. Longer projects are often more complex, harder to plan for, and more vulnerable to inflationary pressures, making accurate long-term cost estimation particularly challenging.
“Risk = Probability of Dam failure X consequence of Dam failure”
The purpose of risk assessment is to help people and organizations better understand the various measures that can be taken to reduce the risks of and improve resilience to dam failure. These measures can be taken by individuals, dam owners and dam operators, organizations, communities, relevant state and local agencies, or tribes. This section provides an overview of the risk reduction measures for consideration and use based on individual situations and provides resources with more information.
Risk reduction measures aimed at reducing the likelihood of a dam failure and improving the resilience of those impacted by a potential dam failure should be tailored to the needs of all stakeholders. Stakeholders must understand their roles and responsibilities to ensure effective risk reduction and incident management. One of the initial critical steps is identifying the at-risk population and understanding each stakeholder’s mission, objectives, obligations, and expectations for risk reduction. Ensuring effective communication among stakeholders will improve coordination among the various entities, particularly following a dam failure. The actions can be categorized according to the event scenarios as seen in the image below.
Earth Dam Risk Mitigation Chart
We go into further detail about dam disaster risk mitigation in the following sections:
Many entities from federal to local are involved in and responsible for dam safety planning activities. These activities serve a wide variety of purposes, from long-term resilience to short-term emergency response. Many types of stakeholders may find it advantageous to conduct a risk assessment. A risk assessment identifies potential hazards and analyzes what could happen if a hazard occurs. The methodology and information included in the assessment will vary depending on hazard types and mitigation measures used in the pre-planning processes.
It is important for those involved in risk management of dams (owners, regulators, state and local officials, and individuals, among others) to understand the all necessary actions to ensure dam safety and the extent of the evacuation needed for particular scenarios. An evacuation may be triggered by a catastrophic dam failure, but it could also be necessitated by the activation of an emergency spillway. Both scenarios may have different inundation and evacuation maps. Details related to different failure scenarios and dam releases should be outlined in the Emergency Action Plan (EAP) / Emergency Operations Plan (EOP). All appropriate stakeholders should be involved in dam safety and crisis response.
Important Terminology – As defined by the Federal Emergency Management Agency (FEMA)
Planning activities, including developing an Emergency Action Plan, should be performed by dam owners and operators. Serving a wide variety of purposes, from long-term resilience to short-term emergency response, many entities are involved in these activities.
The following advisory presents several suggested planning activities. However, it is not intended to be inclusive of all planning that could be performed by stakeholders to reduce the risk of a dam failure, prepare for potential dam failures, and improve response and recovery activities should such an incident occur.
Suggested Types of Planning Actions (source):
Preparedness
Operational
Mitigation
Security
Zoning
Emergency Operations
An Emergency Action Plan (EAP) is vital for every dam to ensure a swift response in emergencies. Effective communication and coordination among emergency management agencies and stakeholders are key to minimizing damage and saving lives. Regular training and inspections are crucial for preparedness.
Every dam should have an Emergency Action Plan, regardless of their hazard potential. An EAP is a formal document that identifies potential emergency conditions at a dam and specifies actions to be followed to minimize the loss of life and property damage.
Emergency Action Plan
Conduct Training
Conduct Dam Inspections
Conduct a Dam Evaluation
Perform Operations and Maintenance
Perform Needed Mitigation
Dam hazard potential classifications are important to know because the hazard potential classification may impact the mitigation solution. The possible classifications include low hazard potential, significant hazard potential, and high hazard potential. They are each defined as the following:
Forecasting and pre-emergency warning systems and emergency action for dam owners and operators can be used.
Post-event data are especially critical for risk assessment. To be better prepared for a dam safety incident, stakeholders can improve their understanding of potential consequences of an incident, including an
unplanned large reservoir storage release or failure scenario for a particular dam and the probability for a given event scenario (e.g., mechanical failure; inoperative gate or valve; trash rack or inlet clogging) at that specific dam. Post event recovery can be done by collecting accurate data that provides additional insight to the dam’s design, condition and performance, and effects on downstream assets by:
With this information, dam owners can develop dam-specific plans and establish memorandums of agreement so they are better prepared to respond to emergency incidents. In addition, communities can include this information in mitigation plans, land use plans, a dam-specific annex to their Emergency Operations Plan
There are some evaluation conducted as part of post event learning, particularly related to improving emergency performance for future events.According to the research study, there are five main types of formal post-event emergency management evaluation.
Measures considered are those that fall under FEMA’s Category B Emergency Protective Measures.
Emergency protective measures conducted before, during, and after an incident are eligible if the measures eliminate or lessen immediate threats to lives, public health, or safety OR eliminate or lessen immediate threats of significant additional damage to improved public or private property in a cost-effective manner.
A successful dam safety monitoring system consists of the following four components:
This system is ultimately utilized to detect any possible threats to a dam infrastructure, such as floods and landslides.
Visual inspections are a key factor in a dam safety monitoring system. In fact, there are a lot of situations, like the evolution of an important crack, which can only be evaluated through visual inspections.
The engineers check for cracks, bulges and hollows on the upstream and downstream face. Just like landslide the dam could indicate unstable, and there is a possibility that with time, a portion of the slope could collapse. Hollows can also indicate that floodwater has been over topping the dam and gradually eroding the downstream slope. Engineers check signs of water leakage through or under the dam. Leakage through the dam can erode away the material inside gradually creating a large cavity. Eventually, the cavity can collapse in on itself reducing the stability of the dam.
Nowadays new technologies are adopted for a better visual inspection of the dam. Combined laser scanning and digital image technologies are recent fields of research and the use of such technologies will certainly enable the automation of visual inspection data collection. Moreover, this calls for an effective implementation of a visual inspection support system which will enable the identification of deterioration processes in a rather accurate, complete and faster way.
The instrumentation component of a dam safety monitoring system includes sensors for the measurement of key parameters that can be used to monitor the ongoing performance of the dam.
Sensors must be installed in order to undertake the following recommended measurements (Tavares de Castro [28]):
Data collection can vary from manually read instruments to fully automated data acquisition systems. The most appropriate data collection system depends upon the dam safety monitoring objectives. A typical dam safety monitoring system consists of a small number of measurements with fully automated data acquisition, sufficient for allowing a fast and efficient evaluation of the dam safety conditions. This is often complemented by a large number of instruments read by hand-held computers, thus allowing for a better and more complete knowledge of the dam behavior.
Decisions that must be made at the dam site include:
These first three components are generally a responsibility of the dam owner and must be considered in the emergency plan for the dam (Internal Emergency Action Plan ” IEAP). After an emergency event is detected or reported, those responsible for the IEAP must classify the event into a scale of emergency level.
Emergency level classifications are as follows:
For each of these emergency levels the IEAP must provide the following information:
A notification system should be implemented for facilitating communications between the dam owner and the agencies responsible for the dam safety.
The following peoples and groups should be responsible for and involved in the IEAP the notification system:
Flow Diagram of a Fully Automated Data Acquisition, Notification, and Warning System – Click for source
The warning system is commonly implemented in the community that is in the most dangerous zone of the downstream valley. Public warnings can be sent through audible systems such as radio and television, door-to-door warnings, and visible systems like personal direct notification via telephone or cell phones (SMS and notification Apps).
Each system has its advantages and disadvantages.4 However, of most importance is to ensure that the message is easily understood by the public and to guarantee that the system is reliable. For this, false alarms must be avoided and maintenance needs to be efficient.
Public warnings using the Internet and the World Wide Web pages of those organizations in order to expand coverage. Billboards also constitute a simple and inexpensive way of warning but are a solution limited in coverage as traditional boards do not allow for up-to-date warnings. However, electronic billboards are now widely used to issue warning messages to those traveling on highways.
The purpose of an evacuation plan is to relocate people to safe areas whenever their safety becomes threatened, regardless of the hazard. This action implementation is generally the responsibility of the local authorities. A decision should be made to start evacuation either prior to a predicted dam break or immediately in the case of an unforeseen failure. This should take into consideration the celerity of the dam break wave, the distance of the population from the dam, and the reliability of the warning system. In order to ensure efficient evacuations, the nearby population should be educated on evacuation procedures in case of a dam failure. The civil protection teams should also have quality training and there should be an availability of various escape possibilities. Additionally, special considerations should be made for vulnerable persons in affected populations, such as children, the elderly, and disabled people.
Flood water can be one of the most destructive forces on earth, especially if caused by an event that unexpectedly overwhelms an existing flood defense or by catastrophic breach of a dam or levee. Decisions on investing in dam or levee improvements are based primarily on risk to life by applying the concept of tolerable risks. Since informed decisions based on tolerable risk require estimates of loss of life for potential flood events, the focus of this section is on estimating loss of life. Estimation of the magnitude of life loss resulting from a flood requires consideration of the following factors:
Dam failure consequences can be classified as extreme, very high, high, significant, or low. The consequence classification is used to determine the design requirements for a particular dam, with dams of higher failure consequence having higher design standards. In the next section, we explore suggested safety guidelines and inspection procedures for dams falling under the various consequence classifications.
It is helpful to prepare an inspection route in advance to ensure that every part of the dam will be visited. An inspector can take many different approaches to examining a dam, but the selected method should be systematic to ensure that all features are covered and to make the best use of the time available. A recommended sequence to assist with a visual inspection starts at the top of the dam and proceeds downward. Sometimes it may be more efficient to inspect the easiest, or most readily accessible areas first, or those areas of known problems. However, no matter where an inspector is located on the dam or spillway, he should stop periodically and look around 360 degrees to observe other features from that vantage point.
This list provides effective guidelines for routing your visual inspection of a dam.
The general technique for inspecting the slopes of an embankment dam is to walk over the slopes as many times as is necessary to see the entire surface area. An inspector must repeatedly walk back and forth across the slope until the whole area has been viewed, giving greater scrutiny to the downstream slope below the pool elevation. The following two patterns can be used for walking across the slope:
Cracks and slides may signal serious problems within the embankment. Looking for and spotting cracks may be difficult, particularly if the embankment is covered with heavy brush or vegetation. As a result, an inspector must walk along the slope in such a way that all the cracks will be spotted. Embankment slides are usually easy to find. Cracks in the embankment are often the beginning of a slide and further weaken the soil by allowing more water to enter the embankment. Cracks may be only a centimeter or two wide but 0.5 to 1.0 meters deep. Usually, a depth of more than 0.5 meters means that a serious condition is present. Shallow cracks may be harmless desiccation cracks. All cracks over 0.3 meters deep should be closely checked and evaluated.
Cracks on embankments are divided into three categories:
Longitudinal Cracks
Longitudinal cracking may be a sign of localized instability, differential settlement, foundation settlement, and/or movement between adjacent sections of the embankment. In recently built structures, longitudinal cracks may indicate inadequate compaction of the embankment during construction. This form of cracking can occur anywhere on an embankment and is characterized by a single crack or a close, parallel system of cracks along the crest or slope in a direction parallel to the length of the dam.
Transverse Cracks
Transverse cracking may be a sign of differential settlement or movement between adjacent segments within the embankment or the underlying foundation. Transverse cracking is usually a single crack or a close, parallel system of cracks which extend across the crest in a direction perpendicular to the length of the dam. This type of cracking is usually greater than 0.3 meter in depth and can easily be distinguished from drying cracks. Transverse cracking poses a definite threat to the safety and integrity of the dam.
Embankment Slides
Embankment slides have various names including displacements, slumps, slips, and sloughs and can be grouped into two broad categories:
Embankment slides are usually easy to spot and require immediate evaluation by a geotechnical engineer if they are large or are continuing to show movement. Most embankment slides have early warning signs that allow their detection. A bulge in the embankment and vertical displacement at a crack in the embankment are usually signs of sliding.
Bulging of the Dam
Bulging is most evident at the toe of the dam. If an inspector suspects a loss of freeboard (the vertical distance between the maximum water level and the crest of a dam) a survey of the crest should be performed to verify if there has been a loss of freeboard. If this survey confirms a loss, this could indicate a possible dam bulging problem and the probability of dam failure. The area above a bulge should be checked for other indicators of instability such as cracks and scarps. However, not all bulges suggest a stability problem. When the dam was constructed, it may not have been uniformly graded by the bulldozer or grader operator, so there may be bulges in the embankment that were formed during construction. Bulging associated with slides is a more severe problem. If bulging associated with cracks or scarps is discovered, a qualified dam safety professional should be contacted at once
The flood hydrograph (seen below) resulting from a dam breach is dependent on many factors. The primary factors are the physical characteristics of the dam, the volume of the reservoir, and the mode of failure. Characteristics such as dam geometry, construction materials, and mode of failure determine the dimensions and timing of breach formation, volume of reservoir storage, and reservoir inflow at the time of failure; this determines the peak discharge and the shape of the flood hydrograph.
Slope protection is designed to prevent erosion of the embankment slopes, crest, and groin areas. Inadequate slope protection usually results in deterioration of the embankment from erosion, and in the worst cases can lead to dam failure. Inspectors should look for inadequate slope protection, including eroded and displaced materials and lack of vegetation during every visual inspection.
Dam breach parameters, such as breach width (Wb) and breach formation time (τ), are often estimated using regression equations. These empirical models, derived from historical dam failure data, offer simplified methods to predict breach dimensions and failure timing—critical factors in risk assessment. Commonly used regression equations include those by MacDonald and Langridge-Monopolis, Froehlich, and Von Thun and Gillette, among others. Each regression equation is derived based on different assumptions and datasets, which influences the range of dam sizes for which the equation provides reasonable estimates. If a dam falls outside the range of data used to develop the equation, the resulting estimates may be biased or inaccurate. Below, we present the breach parameter equations developed by MacDonald and Langridge-Monopolis in SI units. For estimates in English units, corresponding figures are provided in the paper.
In 1984, MacDonald and Langridge-Monopolis were successful in relating breaching characteristics of earthfill dams to measurable characteristics of the dam and reservoir. Specifically, a relationship exists between the volume of material eroded (Vm)in the breach and the Breach Formation Factor (BFF), which if defined as the product of the breach outflow volume (Vw) and the height of water above the breach bottom (H):
BFF = Vw (H)
Where:
Vw = Volume of water passes through the breach (m3)
H = Height of water (m) over the base elevation of the breach
However, before conducting breach analysis, the exact volume of water outflow (Vm) through the breach is unknown. A common approach is to initially estimate Vw as the volume of water in the reservoir at the time the breach begins. This estimate serves as the starting point for the breach parameter analysis. The estimated outflow volume is then compared with the calculated volume from the analysis results. Based on this comparison, a refined Vw estimate is made, followed by a reanalysis and further adjustments. Through this iterative process, the most accurate estimate is ultimately achieved.
Using the calculated BFF, the volume of material eroded in the breach (Vm) can be estimated as follows:
Vm = 0.0261 x (BFF)0.77 for earthfill dams; and
Vm = 0.00348 x (BFF)0.77 for earthfill with clay core or rockfill dams
Where:
Vm = Volume of material in breach (m3) which is eroded
Using the geometry of the dam and assuming a trapezoidal breach with sideslopes of (Zb :1), the base width of the breach can be computed as a function of the eroded volume of material (Vm)as:
Wb = [27xVm – H2 x (CxZb + HxZb Z3 /3)] / [Hx(C + HxZ3 /2)]
Where:
Wb = Width of breach (m) at base elevation of breach
C = Crest Width of dam (m)
Z3 = Z1 + Z2
Z1 = Slope (Z1 :1) of upstream face of dam
Z2 = Slope (Z2 :1) of downstream face of dam
Zb = Side slope (Zb :1) of the breach, Zb can be assumed to be 0.5 (0.5H :1V) according to MacDonald and Langridge-Monopolic.
If the calculated breach width is negative, then the reservoir volume is not large enough to fully breach the dam and a partial breach will result. In this case, the head of water (H) needs to be adjusted to estimate the breach depth and peak discharge. Maximum breach widths have historically been limited to less than 3 times the dam height (Fread, 1981). In addition, site geometry often limits breach width.
The time of breach development (τ) in hours, has been related to the volume of eroded material. Interpretation of data suggests that the time for breach development can be estimated by:
τ = 0.0179 × Vm0.36 for earthfill dams
The breach parameter estimation provided by MacDonald and Langridge-Monopolis indicates that their equation serves as an envelope equation, which tends to overestimate breach time. Additionally, beyond their regression equation, several other regression equations derived from various dam datasets can be utilized for estimating dam breach parameters. It is particularly important to carefully examine the validity of parameters for larger dams, as most available failure data pertains to smaller dams. If dam dimensions fall outside the range of existing datasets, regression estimations can become unrealistic. In addition to using regression equations, the breach parameter determination process can be enhanced by incorporating geotechnical analyses and qualitative assessments. It is essential to verify these values against the ranges provided in the Federal Agency Guidelines (as shown in the table below) to ensure accuracy.
Table. Ranges of Possible Values for Breach Characteristics
Table: Ranges of Possible Values for Breach Characteristics
To enhance the reliability of the results, it is essential to utilize parameters from multiple regression equations and conduct a sensitivity analysis. Once several sets of breach parameters have been established, comprehensive physically based computer modeling using HEC-RAS can be performed. This modeling will generate different sets of outflow hydrographs for various study areas, which are crucial for assessing the impact of breach parameters on downstream flood.
For effective risk assessment, it is essential to select the most likely breach parameters for each event or pool elevation, relying on engineering judgment. If breach estimates converge on similar flow and stage values at risk locations, a simple mean value can be used. Otherwise, a more detailed selection process is necessary to avoid skewing results.
Once the final breach parameters have been selected, it is essential to conduct several reasonableness checks:
These guidelines are based on the 6.3HEC-RAS Hydraulic Reference Manual. For more detailed information on modeling and methods, refer to the “Performing a Dam Break Study with HEC-RAS” chapter of the manual, which offers a recommended approach and includes an applied example.
A comprehensive Dam Safety Review (DSR) is a procedure for assessing a dam’s safety as an entirety. This procedure comprises a detailed study of dam engineering with specialist support, which includes an assessment of the records and reports from investigation, design, construction, commissioning, operation, maintenance, instrumentation monitoring, and surveillance activities.
The comprehensive dam safety evaluation should be compulsory in the case of:
This comprehensive DSR should be documented in the form of a report that outlines the results of the evaluation and recommends any necessary remedial or maintenance work. Dam owners may use risk assessment techniques with safety reviews to determine the urgency and extent of work needed and to properly prioritize remedial works for their dams.
A Dam Safety Review Panel (DSRP) should be constituted to carry out a comprehensive assessment of a dam system. Although no one defined structure for such a panel exists, every country should have sufficient guidelines and standards for dam safety. Many entities are often involved in ensuring sam safety standards are met. Every safety program should follow basic procedures and address critical safety points.
Comprehensive Dam Safety Review Procedures:
Prior to this evaluation, the DSRP should be provided with various details about the dam so that their DSR is as comprehensive as possible. The technical memorandum should consist of all relevant details, data, and drawings for the dam project that the panel will inspect. This generally includes the following:
A. General Information
B. Hydrology
C. Geology
D. Layout, including Drawings of the
E. Dam and Spillway
F. Reservoir Operation & Regulation Plan
Members of the Dam Safety Review Panel should have sufficient experience in the field of dam safety, preferably in the areas of dam-design, construction supervision, hydro-mechanical engineering, hydrology, geology, geo-technical investigation, embankment inspection, instrumentation, seismic design, dam-rehabilitation, or other related fields such as;
Dam safety inspections are conducted for a variety of reason: to ensure proper operation and maintenance, to discover unsafe conditions and determine why they exist, to recommend remedial measures to mitigate the deficiency or defect that will safeguard the structure and appurtenances, and to confirm that the dam meets minimum State Dam Safety or State Dam Safety Cell requirements.
There are four types of dam inspections, including;
Every inspection should consist of three to five elements, depending on the type of inspection. All inspections should include the first three of the following items. Comprehensive evaluation inspections should include all five.
All dams may require additional comprehensive evaluation inspections on a regular basis for as long as the dam exists. The amount of background information needed and the frequency of inspections and reporting procedures are dependent on a dams hazard classification, its size and type, and current CDSO regulations. For example, high hazard dams that pose a significant risk to downstream property require more detailed background information and more frequent and rigorous inspections as compared to low hazard dams with small reservoirs. Generally, the level of inspection effort should correspond to the hazard potential of the dam.
A scheduled inspection is a preventive measure designed to develop solutions for preventing further degradation of a dam. Scheduled inspections involve reviewing past inspection reports, performing a visual inspection, and completing a report form. These are carried out by a qualified inspection team along with maintenance staff or the dam owner.
Scheduled inspections should include the following four steps at a minimum:
For informal inspections, the evaluation process typically consists of a review of file data such as reports, photographs, monitoring data, visual inspection, and the completion of a report form. An informal inspection can be conducted at any time and may include only portions of the dam or its appurtenant structures. These are usually conducted by project personnel or dam owners as they operate the dam to monitor known problem areas or to provide an update on site conditions between maintenance and comprehensive evaluation inspections.
Conducting a comprehensive evaluation inspection of a dam typically consists of five components:
Comprehensive dam safety evaluation inspections should be the initial inspection for all dams, regardless of hazard classification. From then on, they should be performed on high hazard dams every ten years, unless otherwise required by current regulations. These inspections are typically carried out by a team of one or more professional engineers, geologists, or qualified technicians, accompanied by the dam owner or his representative. The composition of the group is determined by the type of dam and its appurtenant works, as well as the condition of the dam.
Step 1: If a dam has instrumentation, the data and data analyses should be collected and reviewed. If an information database is already compiled in a project file, the first step consists of a file review.
Step 2: The embankment must be stable under all operating conditions, and the spillway and outlet must be capable of safely passing the design flood. The absence or insufficiency of information essential to this part of the inspection (such as foundation characteristics, materials engineering properties, hydrological data, hydraulic analysis, and site seismicity) is noted, and actions required to obtain the information are recommended.
Step 3: The need for more information should be noted in the inspection report. If necessary, supplemental data should be acquired by exploratory drilling, laboratory testing, reference to published hydrological data, estimation, and special studies.
Step 4: Using the available information, analyses, supporting calculations, and field findings, an inspector prepares a list of conclusions and recommendations.
Step 5: The observations made during the field inspection, the analytical findings, conclusions, and recommendations are documented in a comprehensive inspection report that may include appendices for special studies, laboratory and field-testing, revised flood estimates, photographs, and other supporting data.
Step 6: After or during the preparation of the inspection report, inspectors should discuss and share the results of the inspection with dam owners or their representatives. It is important that dam owners are informed and aware of the findings and recommendations, particularly if deficiencies are discovered and repairs or further evaluations are required. Inspectors should encourage dam owners to perform all recommended repairs, evaluations, monitoring, and maintenance within a time that is suitable for the necessary action.
Step 7: The comprehensive evaluation inspection report may need to be submitted to the CDSO for high hazard dams, and for other dams. This step also includes any report revisions that may be asked for by the CDSO. A copy of the report should be placed in the dam owner’s project file.
Step 8: Finally, inspectors should summarize and document any of the dams deficiencies.
Special inspections are not regularly scheduled activities, but are usually made before or immediately after the dam or appurtenant works have been subjected to activities, but they are usually made before or immediately after the dam and appurtenant works have been subjected to unusual high pool level, rainstorm, or a significant earthquake. A special inspection may also be performed during an emergency, such as an impending dam breach, to evaluate specific areas or concerns.
The dam inspectors should be thorough and organized to readily trends, it is necessary to maintain records of performance in an orderly way. Inspectors should be well organized with the instrumentation and tools to be used during the inspection. The facilities should be evaluated at regular intervals and in a format that makes them easily interpreted. If inspectors are unavailable to interpret or evaluate observed conditions, they should seek the advice of more qualified dam safety specialists.
The following section includes content from the “Guidelines for Operation and Maintenance of Dams in Texas” Manual, Chapter 3: Hazards, Risks, Failures.
Natural hazards such as floods, earthquakes, and landslides are major contributors to risk. Natural hazards that threaten the dams include:
Flooding from high precipitation – Of all the natural events that can impact dams, floods are the most significant. Floods are the most frequent and costly natural events that lead to disaster. As a result, it is imperative that flood potentials are included in the risk analysis for dam failure.
Flooding from dam failure – More people and properties are generally placed in jeopardy when a dam fails as a result of a flood than when a natural flood occurs. The sudden surge of water generated by a dam failure usually exceeds the maximum flood expected naturally. The upper portions of an inundation zone almost always exceed the 100-year floodplain considerably. Accordingly, residents and businesses that would escape natural flooding can be at extreme risk from dam failure flooding.
Earthquakes – Dams, both earthen and concrete, can be damaged by the ground motions caused by seismic activity. Cracks or seepage can develop and this can lead to immediate or delayed dam failure. Dams built in earthquake-prone regions such as California should develop their emergency procedures accordingly.
Landslides – Landslides and rockslides may directly impact dams by blocking a spillway or by eroding and weakening abutments. Indirectly, a large landslide into a reservoir behind a dam can cause an overflow wave which will exceed the capacity of the spillway and lead to failure. A land (or mud) slide can form a natural dam across a stream which can then be overtopped and fail. Failure of such a natural dam could then cause the overtopping of a downstream dam or by itself cause damage equivalent to the failure of a human-made dam. Additionally, the large increases in sediment caused by such events can materially reduce storage capacity in reservoirs and increase a downstream dams vulnerability to flooding. Sedimentation can also damage low-level gates and water outlets, and damaged gates and outlets can also lead to failure.
There are many complex reasons, both structural and nonstructural, for dam failure. Many sources of failure can be traced to decisions made during the design and construction process and to inadequate maintenance or operational mismanagement. While failures can also result from the natural hazards already mentioned, for the owner, a dams structure is the starting point for understanding the potentials for failure.
Earth dams are particularly susceptible to hydrological failure since most sediments erode at relatively low water flow velocities. Hydraulic failures result from the uncontrolled flow of water over the dam, around the dam, adjacent to the dam, and the erosive action of water on the dam’s foundation. Once erosion has begun during overtopping, it is almost impossible to stop.
Improve stability:
A falling slope can cause structural instability and this can have dangerous consequences. Dams must be stable and well maintained, if not, a slope failure or other condition can damage it.
Temporary storage is used for floods larger than expected. This is accounted for by using a freeboard. Raising the dam height is necessary to meet freeboard requirements. Increasing the normal pool is not the correct method for mitigation as it raises dam risk by increasing the amount of water stored in the reservoir. An example of this includes using the compacted borrow soil using soil material with very low permeability.
Overtopping can cause extreme erosion of an unprotected or poorly protected embankment dam, which can threaten total breach of the dam and release of the reservoir to the downstream area. This happens when the reservoir water level exceeds the height of the dam crest and water spills over the top of the dam.
Before designing the overtopping protection for an exceeding dam the possible impact of proposed modification must be evaluated. Any reduction to the embankment cross-section can decrease the factor safety for slope stability. Excavation at the toe of the embankment to construct the various features of the overtopping protection, in particular for the construction of downstream stilling basin will increase the stability of the embankment and could increase the potential for internal erosion. An evaluation of the estimated risk of the dam failure during construction should be performed as part of the design of overtopping protection for an embankment dam and should involve geotechnical engineers and geologists.
Overtopping can cause extreme erosion of an unprotected or poorly protected embankment dam, which can ultimately result in a total breach of the dam and the release of the reservoir to the downstream area. This happens when the reservoir water level exceeds the height of the dam crest and water spills over the top of the dam.
There are several methods of controlling seepages.
In order to determine the thickness of grout curtains empirical techniques have been adopted over the past years. There are several methodologies used to determine the thickness of the grout curtain. There are three requirements on the curtain related to the thickness.
Most importantly the requirement related to erosion of fracture infilling material highlights the importance of having knowledge on critical conditions for initiation of erosion.
Dam Failure Mitigation Solutions
The evaluation of a dam will identify problems and recommend remedial repairs, operational restrictions and modifications, or further analyses and studies to determine solutions to problems. A safety program comprises several components for addressing the spectrum of possible actions to be taken over the short and long term.
Developing a safety program involves a phased process beginning with collection and review of existing information, proceeding to detailed inspections and analyses. Most of the preliminary work can be accomplished by the dam owner with the assistance of state and local public agencies. However, depending upon the number and seriousness of problems identified by the initial assessment, professional assistance by qualified engineers and contractors may be required.
The following reference was used to create this comprehensive table.
Problems | Problem Cause | Possible Consequences | Recommended Actions |
---|---|---|---|
![]() | Piping or internal erosion of embankment materials or foundation causes a sinkhole. The cave-in of an eroded cavern can also result in a sinkhole. | Piping can empty a reservoir through a small hole in the wall or can lead to the failure of a dam as soil pipes erode through the foundation or a previous part of the dam. | Inspect other parts of the dam for seepages or more sinkholes. Identify the exact cause of sinkholes. |
![]() | A portion of the embankment has moved because of loss of strength, or the foundation may have moved, causing embankment movement. | Indicates the onset of a massive slide or settlement caused by foundation failure. | Depending on the embankment involved, draw the reservoir level down. A qualified engineer should inspect the condition and recommend further actions to be taken. |
![]() | Earth or rocks move down the slope along a slippage surface because of too steep of a slope, or because the foundation moves. Also, look for slide movements in the reservoir basin. | A series of slides can lead to obstruction of the outlet or failure of the dam. | Evaluate the extent of the slide and draw the reservoir level down if the safety of the dam is threatened. |
![]() | Poor quality riprap has deteriorated. Wave action has displaced the riprap (loose stone used to form a foundation for a breakwater). Round and similar-sized rocks have rolled downhill. | Wave action against these unprotected areas decreases the embankment width. | Re-establish a normal slope. Place bedding and competent riprap. |
![]() | Similar sized rocks allow waves to pass between them and erode small gravel particles and soil. | Soil is eroded away from behind the riprap. This allows riprap to settle, providing less protection and decreasing the embankment width. | Re-establish effective slope protection and place new bedding material. An engineer is required for designing the gradation and size for rock for bedding and riprap. They should also inspect the condition and recommend further actions to be taken. |
![]() | Loss of strength of embankment material. This can be attributed to infiltration of water into the embankment or loss of support by the foundation. | Massive slide cuts through the crest or up-stream slope, reducing freeboard and cross section. Structural collapse or overtopping can also result. | Measure the extent and displacement of the slide. If continued movement is seen, begin lowering the water level until the movement stops. Have a qualified engineer inspect the condition and recommend further action. |
![]() ![]() | Differential settlement of the embankment leads to transverse cracking (e.g., center settles more than abutment). Deformation caused by structural stress or instability. | Settlement or shrinkage crack can lead to seepage of reservoir water through the dam. A shrinkage crack allows water to enter the embankment. This promotes saturation and increases freeze-thaw actions. | Plug the upstream end of the crack to prevent flows from the reservoir. A qualified engineer should inspect the conditions and recommend further actions to be taken. Also stake out the limits of cracking. An engineer should be brought in to determine the cause of cracking and supervise all necessary actions |
![]() | Lack of adequate compaction and rodent holes. Piping through the embankment or foundation can also lead to this. | This indicates the possible washing out of the embankment. | Inspect for and immediately repair any rodent holes and control rodents to prevent future damage. Also have a qualified engineer inspect the conditions and recommend further action. |
![]() | Drying and shrinkage of surface material can lead to longitudinal cracking, as well as the downstream movement of settlement of the embankment. This can also be caused by uneven settlement between adjacent sections or zones within the embankment. | This can be an early warning of a potential slide. Shrinkage cracks allow water to enter the embankment and freezing of this water will further crack the embankment. | If cracks are from drying, dress the area with well- compacted material to keep the surface water out and natural moisture in. If cracks are extensive, a qualified engineer should inspect the conditions and recommend further action. |
![]() | This is usually preceded by erosion undercutting a portion of the slope. It can also be found on a steep slope. | This can expose impervious zones to erosion and lead to further slumps. | Inspect area for seepage and monitor for progressive failure. Have a qualified engineer inspect the conditions and recommend further action. |
![]() | Water from intense rainstorms or snow-melt carries surface material down the slope, resulting in continuous troughs. | This can be hazardous if allowed to continue, as it can lead to the eventual deterioration of the downstream slope and the failure of the structure. | The preferred method to protect eroded areas is with rock or riprap. Re-establishing protective grasses can also be adequate if the problem is detected early. |
![]() | This is caused by the natural vegetation in an area. It can also be a sign of dam neglect and a lack of proper maintenance procedures. | Large tree roots can create seepage paths. Bushes can obscure visual inspection and can also harbor rodents. | Remove all large, deep-rooted trees and shrubs on or near the embankment and then properly backfill the void. All cutting or debris resulting from removal should immediately be taken from the dam and properly disposed of outside the reservoir basin. |
![]() | This occurs when there is an over-abundance of rodents. Holes, tunnels, and caverns are caused by animal borrowings. Certain habitats where plants and trees are close to the reservoir encourage these animals. | This can reduce the length of seepage paths and lead to piping failure. If a tunnel exists through the mast of the dam, it can lead to failure of the dam. | Control and remove rodents to prevent more damage, and backfill existing rodent holes. Determine the exact locations of diggings and the extent of tunneling, then remove the habitat and repair damages. |
![]() | Excessive travel by livestock is especially harmful to the slope when wet. | This creates an area bare of erosion protections and causes erosion channels. It also allows water to stand. The area is then susceptible to drying cracks. | Fence livestock outside of the embankment area. Then repair the erosion protection, such as riprap and grass. |
![]() | This results from vertical movement between adjacent sections of the embankment. Structure deformation of failure caused by structural dress or instability, or by failure of the foundation. | This creates local areas of low strength within the embankment which could cause future movement as well as structural instability of failure. It also provides an entrance point for surface water that could further lubricate the failure plane and it reduces the available embankment cross section. | Excavate the area to the bottom of the displacement and then backfill the excavation using competent material and correct construction techniques, and under supervision of engineer. An engineer should be brought in to determine the cause of the displacement and supervise all steps necessary to reduce danger to the dam and correct the condition. |
![]() | This is caused by rodent activity. A hole in an outlet conduit is causing erosion of embankment materials. Internal erosion or piping of embankment material also occurs by seepage. There is a breakdown of dispersive clays within embankments by seepage waters. | The void within the dam could cause localized caving sloughing, instability, or a reduced embankment cross section. It also creates an entrance point for surface water. | An engineer should be brought in to determine the cause of the cave in and supervise action steps. You should excavate the cave in, slope sides of the excavation, and backfill the hole with competent material using proper construction techniques. |
![]() | This results from movement between adjacent parts of the structure. Uneven deflection of the dam underloading by the reservoir and structural deformation or failure near the area of misalignment are also causes. | Area of misalignment usually occurs, accompanied by a low area in the crest which reduces the feeboard. This can produce local areas of low embankment strength which may lead to failure. | Establish monuments across the crest to determine the exact amount, location, and extent of the misalignment. Engineers should determine the cause of the misalignment and supervise all necessary actions. |
![]() | Executive settlement in the embankment or foundation directly beneath the low area in the crest. Other causes include internal erosion of embankment material, foundation spreading to upstream and /or downstream direction, Prolonged wind erosion of the crest area, and improper final grading following construction. | Reduce freeboard available to pass flood flows safely through spillways. | Engineers should determine low area and supervise all steps necessary to reduce possible threat to the dam and correct conditions. Re-establish monuments across crest of dam and monitor monuments on a routine basis to detect possible future settlement. |
Risk is a term that is commonly considered when discussing dam safety. In the context of dam infrastructure, risk refers to the likelihood and potential consequences of a dam failure or significant incident. Basically, risk in dam safety is evaluated by assessing three key aspects:
Together, these aspects help determine the overall risk by identifying vulnerabilities and estimating the severity of possible outcomes.
Dam Risk Components
Understanding the concept of “risk” is crucial for ensuring safety during dam operation and effectively managing potential hazards. To apply this concept in a practical context, it is important to explore related concepts such as risk analysis, risk assessment, and risk management. In the following sections, we will introduce these key concepts and demonstrate how they collectively support dam safety.
Risk analysis is a foundational process for ensuring dam safety. It forms the basis of risk assessment, providing the critical information needed to evaluate the potential impacts of different hazards. In dam safety, risk is typically quantified using numerical inputs, although qualitative assessments may also be employed when required. The type risk analysis and the level of detail depend on the specific goals of the risk assessment. Generally, risk can be estimated by evaluating the likelihood (probability) of a hazard and the consequences that may follow if a failure occurs. This relationship can be expressed in the following general equation:
Risk = [Probability (P) X Consequence (C)] of potential failure.
Where:
An example of how risk can be applied practically is the Annualized Risk to Human Lives, a common criterion in dam design that focuses on the most critical aspect of dam safety: human life. This analysis considers all failure modes that could result in fatalities. The formula is expressed as the summation of all possible failure scenarios, where the likelihood of each failure is multiplied by the expected number of fatalities associated with that specific scenario:
Risk = Σ(probability of each failure scenario) × (expected number of fatalities for that scenario)
In this case, risk is assessed across multiple failure modes, with particular attention given to the potential loss of life caused by a dam failure. The unit of risk is expressed as fatalities per year.
There are principal methods available for conducting risk estimation
FMEA is a method of analysis whereby the effects or consequences of individual components of failure modes are systematically identified and analyzed. FMEA is based on the following main concepts.
FMEA allows the identification of the effects and chain of events caused by each failure mode of the selected components of the system, such as a dam. It serves to:
By identifying the chain of events caused by each potential failure mode, FMEA supports risk analysis by providing a clear picture of where weaknesses lie and how they might lead to larger system failures.
For assessments focused on identifying issues and reducing risk, a more detailed and comprehensive analysis is typically required. The key process in risk analysis involves reviewing dam performance records, identifying potential failure modes, and describing the resulting damage scenarios. These scenarios are then estimated qualitatively and/or quantitatively. Common types of dam risk analysis include:
Generally, the first step in any risk analysis is identifying the site-specific potential failure modes, which form the foundation for further evaluation. The type of risk analysis used depends on the objectives of the assessment. Dam classification, which indicates the risk level of the dam (e.g., high, medium, or low), may also play a crucial role in guiding the level of analysis required. Further details on this process will be provided in the risk assessment section.
Risk analysis is essential for effective risk-based management. It helps evaluate the potential consequences of management decisions by considering hazards and their impacts over time. The risk value is calculated based on the probability of a failure event and the consequences it might cause, typically expressed over time intervals (e.g. euro per year). The dam risk analysis process consists of three main components:
Risk = P1(load) X P2(response given the load i) X (Consequences given the scenario i)
In risk analysis, accurately determining the likelihood of events and assessing their consequences is essential for making informed decisions and prioritizing risk mitigation strategies.</li.
Dam Break Hazard Analysis (DBHA) is a critical component in preparing for potential dam failures and developing effective Emergency Action Plans (EAP). DBHA identifies the objects at risk within the flood hazard area and estimates the potential consequences of a dam failure. It focuses on understanding the dynamics of water flow or other impounded substances in the event of a dam breach, defining the maximum flood coverage, and pinpointing areas most at risk. Numerical hydraulic models play an important role in these analyses, helping to simulate the flow through a dam breach and the downstream flood propagation. The analysis also estimates damages caused by factors such as flow depth, flood intensity, and the type of material (e.g., water, sediment) released during a breach.
The analysis includes a comprehensive damage assessment for the main flood wave, identifying potential impacts on objects within the flood hazard area and adjacent zones. The specific break cases shall be chosen for the damage assessment together with the dam safety authority. The damage assessment considers the following:
To quantify the damage in the dam break event, the damage equation is applied:
Damage=Exposure×Vulnerability×λ
Where:
The damage equation uses λ to account for how different scenarios can change the impact of a dam break, even if the system and hazard objects remain the same. By considering factors like flood intensity or failure conditions, λ helps adjust the results to show how the damage might increase or decrease in different situations, making the estimation of potential damage more accurate and specific to each case.
Dam break hazard analysis (including, where applicable, waste and tailing dams as well as cases where floodwave calculations are not required as such) shall contain:
The analysis process, similar to the risk analysis process but specifically focused on dam break events and associated flooding, involves the following steps.
An Emergency Action Plan (EAP) is a critical component of disaster management aimed at protecting people and property while mitigating the adverse consequences of emergencies. The results of dam break hazard analysis provide essential information for developing effective emergency action plans. Using tools like Geographic Information Systems (GIS), the analysis data can be digitally mapped, for example, as flood inundation maps or risk maps, which can then be further analyzed to inform response strategies.
The dam risk assessment is typically conducted to recommend a course of action—considering various options—to mitigate or accept risks related to a specific dam, project, or specific safety/operational concern about the dam project. Risk evaluation is a key activity in the risk assessment process. It is the process of quantitatively or qualitatively judging the significance of risk and considering all factors that influenced the decision (e.g. cost, social, environmental and economic impacts, regulated evaluation criteria, etc.). Then providing a frame for decision markers. The risk evaluation stage is the point at which social constraints (e.g. law system, societal risk aversion, and policy of stakeholders) and judgments influence the decision process, explicitly or implicitly. The importance of the estimated risks and associated social, environmental, and economic consequences will be considered.
To ensure dam safety, routine risk assessments are essential. The severity of potential dam failures varies depending on the specific conditions of each dam, influencing the level of safety measures and types of risk assessments required. Dams are commonly classified into three categories based on their hazard potential: Low Hazard, Significant Hazard, and High Hazard. For high-risk dams, advanced risk assessments are conducted to further analyze the dam’s condition and determine the need for further evaluation, risk reduction measures, or remediation. Also, it helps prioritize actions based on urgency determined through the assessment.
An example of how the U.S. Army Corps of Engineers systematically manages risks across its portfolio of dams is shown in the flowchart below. Based on the dam’s condition and risk classification, different types of assessments may be conducted.
For all Corps-owned dams, routine safety activities, including inspections, periodic assessments (every 10 years), dam safety training, and monitoring, are performed. Through periodic assessments, the dam’s risk classification is regularly reviewed and adjusted. If significant risks are identified, operational or maintenance actions can be promptly recommended.
For higher-risk dams, more in-depth studies and evaluations are required:
Tolerable risk concepts are used in risk assessment to guide the process of evaluating and judging the significance of estimated risks obtained from a risk analysis (Munger, et al, 2009).
Tolerable risks can be defined as:
Each of these four conditions of tolerability has implications for dam safety. In a life safety context, the key point in this definition is that a level of risk society is willing to tolerate and is not determined by the dam owner but rather by the society itself.
Many factors contribute to society’s risk tolerance, including:
In a qualitative analysis, risk is usually divided in three zones described as simply ‘low’, ‘medium’ and ‘high’ risk. The estimated risk can then be plotted on a risk matrix.
In quantitative analysis, the risk is illustrated in a risk diagram, showing the annual failure probability (the hazard) and the associated consequences. There are two types of risk curves: (1) the f-N curve, which represents a single failure mode, and (2) the F-N curve, which represents the cumulative risk from all failure modes.
The F-N curve, discussed below, shows N as the consequence level and F as the cumulative frequency of all failure events at that consequence level, expressed as an annual probability. In a quantitative risk diagram, at least two risk zones are identified: acceptable risk and unacceptable risk, with a tolerable risk zone in between. The tolerable risk zone is defined by a set of international acceptance guidelines, though risk acceptance criteria may vary slightly between countries.
It is important to note that the lower-right area of the risk diagram represents Low-Probability, High-Consequence (LPHC) events. These events are rare, but if they occur, they can cause severe damage. Due to their rarity, there are few historical examples to guide management, making these hazards particularly challenging to address.
Both the risk matrix and risk diagrams provide a snapshot of the risks associated with a dam, helping to better understand the potential consequences of a dam failure. To create the F-N risk diagram for a dam, factors derived from the quantitative risk assessment are required. This assessment quantifies:
By considering all failure modes and accumulating the failure probabilities of each under their associated potential consequences, a F-N risk diagram is plotted. This diagram represents the total hazards that impact on the whole society and highlights areas of social concern, which may prompt political action. Additionally, risk diagrams allow for easy comparison of dam safety levels and alignment with risk acceptance criteria.
*Note: Even after remediation actions are implemented, residual risks may still remain. These residual risks must be evaluated during risk assessments and cannot be assumed to no longer exist.</p
Risk management is the process of identifying, assessing, and controlling risks to make informed decisions that minimize those risks. Integrating earlier concepts, risk management connects the result of risk analysis and assessment with the development of mitigation strategies to effectively reduce risks.
The framework for dam risk management below illustrates the relationships between key components. Through risk assessment and management, decisions can be made regarding dam safety, necessary actions to reduce risks, and prioritization based on the urgency of the risks. A crucial component of effective risk management and decision-making in dam safety is risk communication, which involves engaging stakeholders and communities that may be impacted by dam hazards.
The main activity of risk management, particularly for high-risk dams, is risk reduction. Based on the risk estimates and evaluations from earlier stages, decisions are made to implement measures such as structural or non-structural actions, enhanced monitoring, additional investigations, remedial actions, or even abandonment of the dam.
To reduce the risk associated with potential dam failure and improve safety in the downstream valley, there are two key strategies must be considered:
Integrated Dam-Valley Risk Mitigation
From both the dam and downstream valley perspectives, these strategies work together to mitigate the hazards posed by a potential dam failure. The integrated concepts of dam safety risk mitigation are presented below
Laws and regulations on dam safety vary from state to state in the US(50 states). The federal emergency management agency (FEMA) administers the national dam safety program, which coordinates all federal dam safety programs and assists states in improving their dam safety regulations and programs. FEMA(2015) presented the “Federal Guidelines for Dam safety risk management” with guidelines for dam risk management. The guidelines provide the general principle for risk management and risk informed decisions. Guidelines for dam safety were published jointly by the U.S Bureau of Reclamation (USBoR) and the U.S Army corps of engineers (USACE).
The overall objectives of dam safety risk management guidelines are guided by the following principles:
Risk assessment comprises six main tasks:
ISO Framework For Risk Management In 2009
Risk identification: Select the level of detail and complexity for the analysis; identify potential failure modes by examining all potential triggering mechanisms; list the consequences of a hazard, including loss of life,
property damage, environmental or social damage, and any other losses.
Risk analysis: identify the risk qualitatively or quantitatively by evaluating the hazard (probability of
events) and consequences with some metric for each and all plausible failure modes; present the result
in a risk diagram.
Risk evaluation: Compare the estimated risk with risk acceptance guidelines from standards according to other countries’ risk evaluation techniques.
Consider computed risk for other dams, other facilities, and dam failure statistics.
Risk treatment: Consider the risk reduction potential methods and do a cost-effectiveness analysis of risk mitigation measures.
The following principles apply to risk assessment according to (FEMA, 2015):
.results of a risk analysis as a key input, but other factors, such as the uncertainty and confidence in the risk estimates, should also be considered;
Join Risk Management Process Adapted by FEMA, USACE, USDI, FEDC and TVA In The USA – Click for Source
The most obvious and direct factors that enter into the assessment are the results of a risk analysis. These results may come in the form of quantitative/numeric results or qualitative statements that indicate the measure of concern relative to public safety. Quantitative results provide three measures related to risk. They are:
However, there are many factors that may be included in a dam safety case and can be considered in the decision recommendation. They include:
This method has the advantage of providing a more consistent basis for decision-making. Also, since it is risk-informed, rather than risk-based, it allows for other important factors (such as those listed above) to be considered in the decision, beyond a sole reliance on numerical risk estimates. The factors that are considered in making dam safety decisions will be at the discretion of each Federal agency.
As managing large dam portfolios requires efficient allocation of limited resources, the dam categorization table below helps prioritize dam safety actions.
Take immediate action to prevent failure. Communicate findings to potentially affected parties. Implement interim risk reduction measures. Ensure that the emergency action plan is current and functionally tested. Conduct heightened monitoring and evaluation. Expedite investigations and actions to support long-term risk reduction. Initiate intensive management and situation reports.
Urgency of action | Characteristics and consequences | Potential actions |
---|---|---|
I Very high urgency | Critically near failure: there is direct evidence that failure is in progress, and the dam is almost certain to fail during normal operation if action is not taken quickly or Extremely high risk: Combination of life and economic consequences and likelihood of failure is very high with high confidence | Take immediate action to prevent failure. Communicate findings to potentially affected parties. Implement interim risk reduction measures. Ensure that the emergency action plan is current and functionally tested. Conduct heightened monitoring and evaluation. Expedite investigations and actions to support long-term risk reduction. Initiate intensive management and situation reports. |
II High Urgency | Risk is high with high confidence or risk is very high with low to moderate confidence: The likelihood of failure from one of the occurrences, prior to taking action, is too high to delay action. | Implement risk reduction measures. Ensure that the emergency action plan is current and functionally tested. Give high priority to heightened monitoring and evaluation. Expedite investigations and actions to support long term risk reduction. Expedite confirmation of classification |
III Moderate Urgency | Moderate or high risk: Confidence in the risk estimate is generally at least moderate, but can include facilities with low confidence if there is a reasonable chance that moderate risk estimate will be confirmed or confidence will potentially increase with future study | Implement risk reduction measures. Ensure that the emergency action plan is functionally tested. Conduct heightened monitoring and evaluation. Prioritize investigation and actions to support long-term risk evaluation. Prioritize confirmation of classification as appropriate. |
IV Low to moderate urgency | Low to moderate risk: The risks are low to moderate, and confidence in the risk estimate is high with the potential for the classification to move less urgently, with further study. | Determine whether action can wait until after the next periodic review. Before the next periodic review, take appropriate interim measures, and schedule other actions as appropriate. Give normal priority to investigations to validate classification, but do not plan for risk reduction measures at this time.Determine whether action can wait until after the next periodic review. Before the next periodic review, take appropriate interim measures, and schedule other actions as appropriate. Give normal priority to investigations to validate classification, but do not plan for risk reduction measures at this time. |
V No Urgency | Low risk: The risks are low and are unlikely to change with additional investigations or studies. | Continue routine dam safety risk management activities and normal operations and maintenance. |
To prioritize actions within a category, consider each of the following factors that can increase the priority of actions at a given dam:
Effective communication is crucial in dam safety, especially in addressing the sensitivities associated with risk analysis. This communication should include potential failure modes, risk analysis considerations, results, decisions, and remaining risks, ensuring that all stakeholders, from technical personnel to the public, comprehend the risks and safety measures. Key communication types include internal communication within dam safety organizations, interaction with owners and stakeholders, and outreach to the public and affected organizations. This section focuses on communication through Emergency Action Plans (EAPs), emphasizing their role in effective risk communication and emergency preparedness. EAPs are vital for mitigating the consequences of dam failures, helping to save lives, reduce property damage, and enhance community resilience. The section outlines the key components of EAPs, beginning with the identification of potential emergencies, followed by considerations for EAP preparation, and detailing the EAP response process.
A dam safety incident is an impending or actual sudden uncontrolled release of water from the structure. The release of water may endanger human life, downstream property, or the operation of the structure. The release may be caused by damage to or failure of the structure, flood conditions unrelated to failure, or any condition that may affect the safe operation of the dam.
Failures attributed to overtopping result from the erosive action of uncontrolled flow over, around, and adjacent to the embankment. On ce erosion has begun during overtopping, it is almost impossible to stop. For this reason, detection and monitoring of reservoir pool levels as well as emergency intervention is important.
This page was created primarily from the information presented in Bill Mollison’s “Permaculture: A Designers’ Manual”, Geoff Lawton’s online Permaculture Design Course (PDC), and the talk by Zachary Weiss that was part of Paul Wheaton’s PDC. Here are some other resources we found helpful too:
Creating a water retention landscape is essential to securing a sustainable way of life. Life is centered around water and the strategic installation of earth dams and supporting water features provides water security. Creating a retention landscape with earthen dams serves several life-giving purposes, such as watering holes for wildlife, fire suppression, eco-system creation and support, irrigation, livestock watering, and long-term water storage within the soil. A DIY earth dam construction site currently does not exist, so that is the aim of this site. As we build our own earth dams, we will continue adding information from those experiences so that others interested in installing earth dams have access to all the essential details necessary to do so correctly and affordably.
Q: Where have earthen dams been installed?
There is a mention of several earthen dam installation in Australia on Darren Doherty’s website, which includes Yeoman’s Nevallan, Yobarnie Farms, and Falloon’s Taranaki Farm. Andrew Millison of Oregon State University’s Ecampus mentions some implementations in the US, such as Seven Seeds Farm and Wolf Gulch Farm. Sepp Holzer also built earthen dams on his property in Tamera and Krameterhof and Geoff Lawton has built several earth dams on Zaytuna Farm.
Q: What is the best way to compact the soil?
By using a rolling compactor (or track roller). A vibrating sheet foot roller is ideal if there is any doubt about sealing a dam.
Q: How many dams should my property have?
Have as many small earth dams as are practicable scattered throughout the landscape, some up high to harness water energy potential and some down low to support livestock/irrigation.
Q: How can I be sure my soil is good enough?
A geotech engineer could be hired for $200-$2000 who could assess the soil for its clay content and give you an accurate assessment of the structural integrity of the soil that is to be used for the earth dam and pond bed. They also provide a spec sheet that can be helpful to mitigate any unpredictable legal issues.
Q: What is the most common problem with energy efficient gravity systems?
Air locks are a common problem. From Wikipedia: “An air lock (or vapor lock) is a restriction of, or complete stoppage of liquid flow caused by vapor trapped in a high point of a liquid-filled pipe system. The gas, being less dense than the liquid, rises to any high points. Flushing the system with high flow or pressures can help move the gas away from the highest point, or a tap (or automatic vent valve) can be installed to let the gas out.”
Q: What happens if the dam begins filling as it is being dug and built?
It sometimes happens that dams fill up with water naturally very quickly and that is usually fine. A dam filling slowly while you are building it is ok.
Q: What can I expect from earth workers during construction?
During construction they used a few heavy machines, such as an excavator to dig trenches and build the dams. Lawton just had to mark the area with pegs. He found that it was easier if the excavator has a 45 ram bucket (made for golf course landscaping), because it can do a lot more with less positioning. Operators are skillful people. From Lawton’s experience the process begins the same way every time – pace around first becoming familiar with how much the other knows. Use lots of pegs so they have the information they need to get the job done accurately. Let the operator know that he/she can take his time and can put shape and form for an artistic touch. They appreciate this, because most sites want them on and off quickly. A good bulldozer driver minimizes movements to those solely used for positioning. A measure of how good they are, is cubic feet of dirt moved per unit of time. To test their skill, get them to pile up soil and spread it evenly without pulling the soil backwards – this needs to be done with feel and without back-blading.
Q: What is a stew pond?
A stew pond is a pond in a cluster of three synergistic ponds. This is a concept that includes three dams – a large, medium, and small. The large and medium dam are alternated between cattle and baby fish – cattle are allowed to wallow in one of the dams for some time and then the cattle are removed and a crop is sown and young fish are introduced. While the other dam is used to grow forage for the cows. Once the forage for the cows have matured, the cows are brought back and the mature fish from the other dams are placed into the smallest of the three ponds, called the stew pond. Here the fish mature until they are ready for the kitchen.