In this paper, we review geomembranes already used in basal structures in the mining industry worldwide, with the main aim of identifying design requirements, guidelines, or recommendations for the use of geomembrane structures. First, we review the literature on how widely geomembrane liner structure are used in mines and their intended purpose, and on how to achieve early involvement and integration of geomembrane structure design in the planning process. We then outline the structural requirements for geomembranes and for the structures above and below geomembranes, and possible restrictions on the use of geomembrane structures (such as water storage, the disposal technique used, and the material to be dumped on top of the geomembrane). Finally, we present a framework for design for geomembrane structures and discuss limitations and prospects of geomembrane-lined tailings ponds. Figure 2 illustrates the research process.
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Typically, development and planning of industrial projects follows an &#;the over-the-wall&#; approach, where design proceeds step by step. Plans are drawn within different design disciplines and given to the next designer or customer in the &#;chain&#; until the plans are complete [ 28 ]. This practice leads to sub-optimization, as different phases, design areas and stakeholders strive to optimize only their own view and performance [ 29 ]. A more holistic approach to tailings ponds project management is clearly needed to utilize the accumulated knowledge. It is particularly important for geomembrane design to be considered and integrated at an early stage, because its importance for the overall solution costs and life cycle costs.
While basal structures of tailings ponds have been improved, problems relating to harmful seepage waters have not been entirely solved. In recent years, leakages have occurred even through geomembrane-lined basal structures meeting the new requirements for mining operations. For example, at the Talvivaara mine in Finland, which was opened in , leakages were detected in , , and , at the Kittilä mine in Finland, also opened in , leakage was reported in , and at Kokoya Gold Mine, Liberia, opened in , the latest liner failure was reported in [ 25 27 ].
Because awareness of environmental impacts has increased and the legislation on basal structures has generally become stricter, in some cases an artificial liner in the foundation design is required to prevent seepage of water from tailings ponds. Positive effects of lining systems with low water permeability in landfill structures have been reported and have affected the requirements regarding foundations in mining areas in Europe [ 11 15 ]. The functionality of basal linings has been widely studied [ 16 24 ] and both national and international design guidelines (e.g., European Council Directive /31/EC, Government Decree on Landfills 331/) are available for landfill basal structures. In the mining industry, however, the legislation regarding basal liners structure is less cohesive and requirements vary between different countries. In Europe mine wastes are regulated under Directive /21/EC. Otherwise, there are country-specific laws and guidelines, which poses challenges for the mining sector since mining companies are typically international.
In conventional disposal systems, tailings are dumped in ponds as a slurry with a solids content of 20&#;40% by weight relative to the total weight [ 11 ]. In a typical case, the tailings ponds are located within peatland areas, in valleys, or on hillsides worldwide. The objective is to utilize natural soil layers with low water permeability (such as peat and glacial till) and local soil formations to reduce the risk of pollution to the environment. The mode of operation of these ponds is seepage of water from the ponds and its collection in a nearby ditch or other drainage structure. One of the greatest environmental challenges arises with tailings that create an acid environment [ 12 13 ]. Acid is formed through the oxidization of minerals containing sulfur (e.g., pyrite) and can have significant effects on surface waters and groundwater in the mine surroundings, where screening, recovering and treating these waters may be difficult and expensive [ 12 ]. Because releases of acidic mine drainage (AMD) into the environment are not desirable, control of the water within stored tailings is essential. The first priority is to prevent formation of AMD but in many cases an impermeable basal layer may need to be constructed ( Figure 1 ).
Impoundment of tailings generally poses one of the most significant environmental risks associated with mines [ 6 ], with the risk closely linked to the type and quality of tailings. Since each mine is unique, the physical and chemical quality of the tailings varies. Typical tailings can be of the same consistency as fine sand, loamy sand, or sandy loam, and they may contain chemical residues from mineral separation or from the coagulants and flocculants used in water separation, e.g., [ 7 ]. The particle properties differ from those of natural soils because the grains in tailings are jagged in shape, while natural loam grains are rounded. High angularity, grading characteristics and loose depositional state of tailings have direct effects on increasing compressibility compared with natural soils [ 8 ], but also on susceptibility of liquefaction of tailings [ 9 10 ].
The use of geosynthetics in industrial applications has become common since the s [ 1 ]. There is huge potential to use these in different mine-related applications, e.g., as geomembranes, plastic pipes, geotextiles, geosynthetic clay liners (GCLs) and reinforcements. The first major mining application was for lining process ponds and as partly impermeable basal structures for solar ponds at the Tenneco Minerals mines in Utah, USA, and at a Sociedada Quimica y Minera mine in Northern Chile at the beginning of the s [ 2 ]. By the late s, geomembranes were in general use in the basal structures of heap leach pads, but they have only become widely been used in the basal liner structures of tailings ponds and waste rock dumps during the past 20 years [ 2 5 ].
Based on the above ( Section 2.1 Section 2.2 and Section 2.3 ), the importance of geomembrane-lined tailings pond as a stakeholder arises from its major role in reducing the environmental footprint of the mining industry. First, the usage of geomembrane-lined basal structures is known worldwide, but all the structures described in the literature are more or less unique. Second, although landfill construction protocols set detailed instructions and design guidelines for geomembrane-lined structures under landfills, mine tailings exert different stresses on the basal structure compared with landfills. Therefore, the exact same construction or design guidelines cannot be used. Third, the climate characteristics pose challenges in design and construction to which attention must be paid. In traditional linear construction project model, participants and stakeholders do not work together at a sufficiently early stage. Many different experts are needed to solve the challenges and balance requirements for success in the demanding construction project. Thus, it is justified to use an advanced project management method like DfX for handling holistic plans to achieve the best available structure.
In complex industrial projects, it is crucial to analyze the stakeholders according to the project&#;s specific areas and aims. One way to analyze the importance of project stakeholders is to consider the salience of the identified stakeholders [ 51 ]. In addition to salience, it is vital to evaluate the stakeholders&#; roles within the project and ensure that different disciplines (stakeholders) work concurrently in collaboration. The overall aim is to integrate all stakeholders and balance their needs and requirements at an early stage. The idea is to involve disciplines or stakeholders in the same process and consider all life cycle issues affecting the project [ 52 53 ]. At present, there may be a risk of the opposite, i.e., a tendency to rush into the details of the design without a proper understanding of the premises. Therefore, a systematic approach is required for organizing the entire design process. This systematic approach must describe stakeholder identification, classification, and management. The project must be organized and controlled by a project management team or project core group with a comprehensive understanding of the project and with the power to steer and manage the project.
Design for Excellence (DfX) is a widely used logic on early involvement and integration. It has been applied for decades in the manufacturing industry, especially in the context of product development projects. DfX is a structured approach for systematic assessment of early product development and functional integration. In DfX, the X stands for an area of design, aspect, or a stakeholder, such as manufacturing, environment, maintenance, supply chain, cost, and so on [ 46 50 ]. In other words, X can be any aspect considered critical for the project. The basic logic of DfX is that &#;X&#; sets requirements, guidelines, and recommendations for design and development. For example, sourcing (design for sourcing) aims for material harmonization and outlines which materials and suppliers are on the list of recommended materials [ 50 ]. The present study analyzes &#;design for geomembrane structures&#;.
One of the primary difficulties in project management arises from who to involve and how to involve them. Stakeholder management has several methodologies for identification, analysis, and prioritization of key stakeholders. Early influencing requires project management to identify and involve key stakeholders at the beginning of the project, enabling them to make an early contribution [ 49 ]. In the present analysis of the importance of geomembranes in basal structures in the mining industry, we consider geomembrane-lined tailings pond as an important stakeholder for early involvement and integration.
Traditional design and construction in tailings ponds projects are typically carried out in linear order, where design and construction proceeds step by step. However, the early phases of the design stage provide the best possibilities to influence the plans and ultimate project success, in the present case in terms of the quality and efficiency of geomembranes in tailings ponds. It applies on both; on contributing to the project aims and solutions, but also reducing the total cost and environmental effects of the project in the later phases of its life cycle. [ 46
In the mining industry, geomembranes and other geosynthetic products used in basal structures face harsh conditions that are not comparable to those in other industrial applications or landfill constructions [ 30 43 ]. These conditions include unusual process conditions, such as high pressure (up to over 3 MPa) directed at the geomembrane, high or low temperatures, air injection, and use of different chemicals. In addition, mines are often located in geographically and climatically extreme or remote areas, such as cold, dry, sunny, or rainy areas or on high ground, making selection of materials and installation techniques challenging. The operating conditions can cause additional stress on materials, which may lead to faster wear and weakening of material properties [ 43 ]. These harsh conditions drastically differentiate the disposal sites in mines from the disposal sites for municipal waste. According to Garrick et al. [ 42 ], the most significant differences between facilities for disposal of tailings and those for municipal waste disposal are:
The most common application for geomembrane basal structures is probably heap leaching, at least in the United States and South America [ 30 ]. Rowe et al. [ 31 ] studied 92 different heap leaching projects in 15 countries (Argentina, Brazil, Chile, Columbia, Philippines, Ghana, Indonesia, Mexico, Namibia, Nigeria, Peru, Poland, Turkey, the United States, and Uzbekistan). Published studies on the application of geomembranes in tailings ponds are fewer. The largest single application in Europe may be the tailings pond at the Lisheen Mine in Ireland [ 32 ]. Some corporations, e.g., Alcoa World Alumina [ 33 ], have published guidelines, including a recommendation on use of geomembranes for the disposal of bauxite tailings generated in aluminum works on purpose-built disposal sites. According to the literature and reports, various examples of planned or built geomembrane-lined tailings storage facilities can be found around the world ( Table 1 ).
Based on our review of critical factors for design ( Section 3.1 Section 3.4.3 and Section 3.4.4 ), use of at least the single-composite liner structure or, in very harsh conditions, the double-composite liner structure is recommended. The single-composite liner structure secures functionality with the geomembrane layer, but also with a sufficiently thick and compacted natural mineral soil layer. The single-composite liner and soil layers work together, so that if one fails the other stabilizes and prevents uncontrolled water flow from the base of the pond. Therefore, attention has to be paid to modeling of seepage water routes and the stability of the dams and foundation. Selection of a suitable geomembrane is also important, as is taking into account the properties of the layers below and above the geomembrane liner. Quality assurance of construction plays a major role in achieving an undamaged and well-functioning structure. In the final phase of the project the tailings pond will be rehabilitated, and the design needs to take into account also the closing arrangements already at the beginning of the tailings pond planning process.
Tailings ponds usually require a closure plan [ 92 93 ]. The basal structure of the pond may affect the design and costs of closure, as well as the available closure methods. If the aim is to build a compact surface over the pond, it must be possible to reduce the hydraulic pressure in the pond and to remove all free water. This can be challenging if drainage solutions are not considered when designing the geomembrane-sealed pond. Dewatering of tailings is also challenging but, according to Bourgès-Gastaud et al. [ 94 ] new innovative cost-efficient drainage possibilities for harsh dewatering cases would be helped by using electrokinetic geocomposite. The function of a compact surface is, above all, to prevent long-term environmental impacts and formation of AMD. AMD develops when water flows over or through sulfur-bearing materials, forming solutions of net acidity. The only way to stop its formation is to prevent sulfur tailings coming into contact with oxygen. Depending on the closure method, harmful AMD can be neutralized or seepage containing the acid can be collected. The closure costs may be high, and the mining operator should be prepared for these expenses [ 93 ]. Increasingly stricter laws have been developed to improve the technologies used, e.g., thickening tailings and paste [ 6 30 ]. In a good design, various alternatives are considered and compared from the perspective of the entire life span of the mine [ 95 96 ].
Normally, impoundment of tailings demands huge earth dam structures, and those dams are typically raised during production. Tailings dams can be raised by three options: upstream, downstream and centerline. A starter dam is typically constructed as a normal earth dam, using natural materials, but dam raisings involves use of tailings. It is economically sound to raise the dam using the upstream method, to decrease the material and space requirements, but in terms of stability issues the upstream method is the most challenging option [ 88 ]. Concerns arise because of poor management, using tailings and mining waste residues, and having raisings located above the stacking. Dam failure mechanisms have been described [ 88 89 ]. The selected method may increase the risks of liquefaction of tailings, a phenomenon which is poorly described, making risk estimations difficult [ 83 91 ]. Foundation properties also affect the failure risk of dams, e.g., due to the drainage arrangements, and special attention has to be paid to estimating the stability of tailings ponds in every step of the life cycle [ 88 ].
Garrick et al. [ 42 ] and La Touche and Garrick [ 80 ] calculated the seepage rates from tailings ponds and compared different scenarios. Their calculations and modeling results showed that when the quality assurance level is excellent, loss of seepage waters into the environment can be limited efficiently through composite structures (geomembrane and bentonite liners) [ 42 80 ]. According to Garrick et al. [ 42 ], the performance of HDPE liners is extremely sensitive to defect occurrence rates, and is thus highly dependent on liner manufacturing and construction quality. Their calculations indicated that a single HDPE liner requires construction to the highest CQA standards to be of significant benefit in reducing the seepage rates of a tailings pond and that, even when the CQA standard is &#;good&#;, the liner can have higher hydraulic conductivity (>1 × 10m/s) than the tailings on top of it [ 42 ].
Accurate estimation of the surface level of seepage water at dam structures is extremely important, making it one of the basic elements in the design of tailings ponds or similar types of dams. Geomembrane liners are increasingly being used in pond basal structures, and other calculations should also be performed. These include modeling seepage routes and rates, and estimating the ability to prevent or minimize leakage throughout the life cycle of the mine. Analytical methods are usually used in calculation of the specifics [ 79 ], while numerical modeling is used in assessing the behavior of the entire pond or the movement of seepage waters [ 80 82 ]. Analytical calculations are based on the theory of fluid movement in pipe systems (Bernoulli equation) and the flow of a fluid through a porous medium (Darcy&#;s law). Many studies have also developed empirical formulae for leakage calculations in various composite solutions [ 81 87 ]. Sufficient modeling accuracy can often be achieved by 2D examination, but 3D modeling is required when, e.g., modeling groundwater head beneath the facility of valley fill [ 42 ].
Quality assurance activities largely revolve around testing the integrity of the geomembrane seams, even though these seldom fail [ 19 ]. The greatest risk has been found to be in installation of the protective layer on top of the geomembrane liner. To avoid construction-related damage when the pond is in use, quality assurance activities should focus more on the detection of leaks. In the USA, geomembrane integrity methods are described in ASTM D standard, which is also applied in Europe as there are no equivalent standards available [ 70 ]. Electrical leak location technologies (ELL) are technologies available for monitoring leakages in the geomembrane lined structures and several standardized methods are available [ 71 76 ]. The sensors measure changes in the resistivity or dielectric property of the soil, which can indicate leakage processes [ 77 78 ]. The monitoring of covered geomembrane structures requires specific methods where grip pattern is installed throughout the survey area, described more closely, e.g., by Gilson-Beck [ 77 ]. According to Gilson-Beck [ 77 ], covered geomembrane structures should be inspected after material placement to avoid later environmental consequences and ELL methods could be adopted as a common method of locating holes during construction, e.g., seam testing in CQA process. The advantages gained with the installation of continuous ELL monitoring to the basal structure of a tailings pond, however, needs further studies. Lupo and Morrison [ 43 ] list the most important points to be taken into consideration in quality assurance as:
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The drainage layer is usually part of the protective layer and generally consists of a natural material, such as sand or gravel [ 43 ]. The hydraulic conductivity of the drainage layer has to be high to maintain a steady flow and preventing clogging of the drainage layer. Moreover, the layer has to be sufficiently strong to take the load placed on it without disintegration [ 30 ]. The drainage layer can also contain pipes, and these pipes have to withstand the conditions in the pond. Problems due to pipes collapsing or becoming blocked have been reported [ 60 69 ]. Lupo [ 5 ] discusses factors affecting selection of underliner and overliner materials, as summarized in Figure 8 . Overall, the entire liner system has to be considered when choosing the materials for the foundation. If design tests indicate that the structure will not function properly with the selected materials, other materials need to be considered ( Figure 8 ).
Because the overliner layer protecting the geomembrane may have several purposes, it can be composed of one or several separate layers. In double-composite structures, for example, the overliner layer provides protection and also functions as a leak detection layer [ 30 ]. However, the most important task of the overliner material is to protect the geomembrane liner from the stress caused by the materials above it. The protective material can be sand, gravel and loam or, in some cases, even soil containing clay [ 43 ]. As long as its stability is not at risk, the protective layer can also contain geotextiles. The thickness of the layer can vary, depending on the load to the geomembrane, from under 1 m to up to 5 m if heavy vehicles drive on it [ 31 ].
The importance of the overliner is sometimes ignored during design, and only the geomembrane material and the hydraulic conductivity of the underliner layer are considered. For example, Rowe et al. [ 31 ] tested the impact of the underliner material on the puncture resistance of the geomembrane and noted that when the strain rose to 13&#;14%, the underliner material no longer mattered. In fact, the overliner material was suspected to have a greater impact.
The above applies to the selection of material when the subsoil or underliner material is non-cohesive soil [ 43 66 ]. In cases where cohesive material (e.g., clay) or organic matter (e.g., peat) is left at the bottom of the pond, it is important to perform the same field and laboratory tests as for a foundation with good bearing capacity [ 32 43 ]. This is because these soils may not only be compressible, but may also yield and compact over time due to creeping or natural degradation. Reinforcement nets, materials intended for under-soil filling, and concrete structures can be used to reduce the strain on the geomembrane liner [ 41 ].
Lupo and Morrison [ 43 ] propose requirements for the underliner material. The material should be soil containing fines with maximum particle size no more than 38 mm, particles of different sizes should be evenly distributed, plasticity should be over 15, and the saturated hydraulic conductivity should be 1 × 10m/s or less. The benefits of having the geomembrane directly in contact with an underlying layer of soil with low hydraulic conductivity have been stated in several publications, e.g., [ 62 68 ]. The conditions at the site need to be taken into consideration to control the construction costs. If the natural hydraulic conductivity on-site is too high, bentonite can be used to reduce the seepage rate [ 44 ]. The amount of bentonite used in soil improvement typically varies between 3 and 8% of dry weight, but the appropriate percentage has to be determined separately in each case [ 43 ]. Hydrated bentonite liners can also be used, but due to high loads and the compressibility and internal shear strength of the liners, it is important to verify the stability of the solution [ 44 ].
Any geomembrane strain causing consolidation needs to be assessed. Consolidation of the foundation, i.e., the underliner structure, caused by the pond is usually first estimated by calculation, and these calculations are then used to assess the behavior of the geomembrane. A strain of 4&#;8% can be permitted for HDPE and 8&#;12% for LLDPE [ 22 ], although the permissible strain should always be verified with the material supplier. It is worth noting that the consolidation in question is large-scale and that local situations, such as tension caused by point loads, are not taken into consideration.
Selection of an appropriate geomembrane requires a clear understanding of the combined operation of the geomembrane liner and the underliner and overliner layers, as well as the relevant normal and shear loads [ 66 ]. Based on practical experiences, Lupo and Morrison [ 43 ] developed a selection chart to facilitate determination of a suitable geomembrane material (only for HDPE and LLDPE) and its strength ( Table 3 ). The chart takes into consideration the foundation conditions (the bearing capacity of the subsoil), the underliner and overliner materials, geomembrane thickness, and the load directed at the geomembrane.
Geomembranes used in basal structures are typically made from one of the following materials: linear low-density polyethylene (LLDPE), high-density polyethylene (HDPE), polyvinyl chloride (PVC), polypropylene (PP), ethylene propylene diene monomer (EPDM), and ethylene interpolymer alloy (EIA). When choosing geomembrane type, key properties that need to be considered are chemical resistance of the geomembrane, tensile strength, temperature resistance, installation conditions, cost, and previous experiences of its use ( Table 2 ). Bituminous geomembrane (BGM) has been used in the basal structures of tailings ponds in some cases, e.g., [ 36 ], but there are no scientific papers describing experiences of this material [ 30 ]. However, experiences of its use in other applications, such as dams and channels, have been reported [ 62 63 ]. According to Cunning et al. [ 63 ], one of the advantages of BGM is that the choice of the underliner material becomes less critical. Additionally, the material&#;s resistance to low temperatures is good and installation is easier, as it can be done at any time of the year. Other benefits of BGM are high resistance to stress and great resistance to damage [ 64 ].
In addition to the above, the tension and pressure caused by the load and consolidation of the foundation, as well as the stress caused by the chemistry of the seepage water, need to be taken into account in the design [ 5 ]. The water on top of the geomembrane, leak detection/collection of leakage water, and loading and unloading of tailings can damage the geomembrane. This can be avoided using a single-composite structure where both underliner and overliner structures are adapted [ 60 ] ( Figure 7 ). This structure is specially designed for ponds where the tailings are dumped as slurry [ 5 ]. The foundation structure underneath the pond has to be connected to the surrounding dam structure and the function of both structures has to be carefully checked [ 4 61 ]. Actions performed during operation, such as raising of the dam, closure of the pond and post-monitoring activities, need to be taken into consideration.
However, the structures shown in Figure 5 do not take into consideration the layers beneath the geomembrane liner. In , the United States Environmental Protection Agency (US EPA) issued instructions for the basal structure if low water permeability is required ( Figure 6 ). The modified basal structure can be constructed according to one of five different design types: (a) compacted clay without geomembrane, (b) a composite solution featuring geomembrane and a layer of compacted soil with low hydraulic conductivity, (c) two geomembrane liners with a leak detection layer, (d) a single geomembrane liner with an underliner layer, and e) a double composite liner structure with two geomembrane liners and a layer with good hydraulic conductivity properties in between for the detection of leaks, as well as compacted layers with low water permeability [ 58 ].
Designing sustainable tailing ponds requires modeling of seepage water routes, both during operation and on closure of the mine. Initial plans are made on the basis of the original mine design and, as reliable data on more parameters become available, modeling calculation are updated [ 42 ]. The most important factors to be considered are the stability of the dam and the foundation and drainage structures [ 4 ]. The most common structures for tailings ponds are: (1) a structure where the geomembrane liner reaches the top of the dam and (2) a structure where the liner is located underneath the dam and reaches the collection pond for seepage water ( Figure 5 ) [ 4 ]. In the latter case, the drainage layer is above the geomembrane liner, in order to lower the hydraulic pressure caused by capillary water above the geomembrane and to minimize leakage through the geomembrane [ 4 ]. The drainage structure decreases the hydraulic pressure and improves the strength and stability of the tailings.
According to the literature and reports examined, geomembranes are widely used in basal structures of mine basins all over the world. The mining industry has a large environmental footprint and one option to decrease the impacts is to introduce mandatory non-permeability basins. If legislation or other regulations are intended to promote the use of geomembrane liners to reduce seepage through the basal structure, more cohesive construction instructions are needed. In European countries, the construction of landfill sites is regulated through legislation, and the structural requirements, such as layer thicknesses and hydraulic conductivity, are specified. If constructors of landfill structures deviate from the structural guidelines for landfill sites, they must prove that the protection level of the alternative structure is at least on the same level, e.g., [ 97 ]. Similar requirements do not exist for structures used in mine tailings ponds. The majority of the existing structures are qualitative, and layer thickness and material requirements are not specified. Therefore, the required level of protection is often unclear. Because boundary limits for design are normally lacking, one option could be a risk-based approach, e.g., [ 98 101 ]. In the design phase, the relevant authorities could set a limit (e.g., mg/L or mg/kg) on the amount of harmful contaminants that the mine operator is allowed to release to the environment. Based on the limit, designers could then calculate the required basal liner structures and dimensions. Possible seepage rates and contaminant concentrations should be analyzed in different scenarios and accumulation of contaminants in nearby surroundings (soil, groundwater, surface water) should be calculated and compared against permit limits considering the whole life cycle of the pond.
There are certain major differences between construction of basal liners for tailings ponds and e.g., for heap leach pads. In heap leaching, the use of geomembranes is justified and even necessary to ensure that metals are recovered as efficiently as possible. Geomembranes are needed to maximize economic efficiency and to prevent transportation of the solution containing metals into the environment. The collection of waters from tailings ponds, on the other hand, does not necessarily increase the efficiency of the process or production. The construction of basal structures and adoption of more complex structures in tailings ponds generate significant extra costs. The leaks that have been detected to date indicate that the structures have to be designed with care and consideration. The reality is that a basal structure lined with a geomembrane will leak at some point in the life cycle of the structure. Leak location technologies could be used to locate failures, although in tailings pond cases, emptying the pond in active phase is challenging and failure repairing is difficult. In heap leach pad cases, the technology would serve more advantages and improve leakage detection and repairing. However, Joshi and Mcleod [ 102 ] found that leakages through the geomembrane in tailings ponds are much smaller than in typical landfill and heap leach geomembrane liner systems. The intended use of the tailings pond has a significant effect on the design of the basal structures. Therefore, changes in the primary purpose of use after construction may create problems if these changes have not been taken into consideration during design. If the selected and constructed basal structures have not been designed for the alternative use, this can have dramatic consequences, e.g., failures.
23,44,81,One of the most significant problems in creating better solutions for the basal structures of mine tailings ponds is that relatively little information has been published on the foundation structures of such ponds. More research is needed, for example on the functionality of geomembrane liners and the underliner and overliner soil, and on related solutions and how the combined operation of natural soil and artificial liners can be optimized through the use of a constructed layer of natural soil or bentonite liners. Some studies, e.g., [ 14 103 ] have expressed concerns about the long-term behavior of clay liners and layers, which are not believed to be as reliable in composite structures as the calculations suggest. Changes in the behavior of clay in the long run cannot be taken into account in calculations, e.g., channels, fissures, or other weaknesses that allow leakage may form. Rowe et al. [ 31 ] tested the functionality of underliner with geomembrane and concluded that further studies are needed on the compatibility of the underliner and overliner materials with the geomembrane, since the maximum allowable strain of 6%, which is generally acceptable for geomembrane liners (HDPE), was exceeded in every test. Brachman et al. [ 104 ] performed similar tests on HDPE geomembrane and concluded that if the geomembrane is not covered with protective textiles and a layer of loamy sand, the risk of puncturing is significant. To improve the safety and functionality of future structures, it is therefore important to collect relevant information on successful solutions and to learn from mistakes.
Early involvement and integration can improve the whole design and construction process enabling management of the most critical areas of design, early enough. By identifying geomembrane-lined tailings pond as a stakeholder with a critical impact on the whole mine, decreases the life cycle costs, improves sustainability and quality of the entire mine. Figure 9 shows major factors affecting the sustainable disposal of tailings, in a framework focusing on the possibilities of influencing the successful project and aiming to prevent conflicts arising later in the process. The key supporting perspectives, from our review, are identified as the mining business, governments requirements, nature, and society ( Figure 9 ). These perspectives were identified from the literature, because international guidelines are lacking, and thus attention must be paid to national instructions and conditions (government requirements). A successful project has to be environmentally sustainable, society&#;s requirements must be heard, and feedback obtained from society needs to be taken seriously. As previously discussed, mines are unique, detailed guidelines are lacking worldwide, and local conditions and material availability differ. Together, these factors form an important part of the framework (nature). Finally, the mining business itself sets the frame for the whole construction process (mining business). Here we outline important perspectives based on earlier research results, but the actual stakeholders and the classifications are project specific, so must identified for each project [see 54]. Based on research on project management, see [ 47 ], it is not sufficient to state simply that tailings ponds are important. Rather, practical tools and methods are needed, especially in complex projects, to enable positive impacts on the final design. Through applying &#;design for tailings ponds&#; as a method, or considering &#;geomembrane-lined tailings pond as a stakeholder&#; it can be ensured that critical factors for tailings ponds are considered from the outset in the design of mines.
Ultimately, the selection of disposal methodology is one more option to alleviate the risk of seepage through the basal structure. To promote the use of more modern disposal technologies, e.g., paste or dry stacking, more experience is needed, especially on the suitability of the method in cold climate regions. Alakangas et al. [ 105 ] reviewed the paste technique and noted that the geotechnical and rheological properties of suitable pastes are well-defined and documented, but that difficulties can arise under cold climate conditions. Snow and ice, together with freezing and thawing cycles, can cause problems, e.g., for pipes, deposition, slopes, and stability, but can also have a positive effect, e.g., by accelerating consolidation [ 105 106 ]. Nevertheless, scientific studies are needed on the functionality and usability of the paste technique in cold climates, and the risks need to be identified and resolved. The presence of snow and ice also affects other disposal methods and makes design, construction, operation and monitoring more challenging.