Impermeable/low permeability systems are needed on mine sites to prevent the unwanted transmission, loss, or release of materials (such as lixiviating fluids, leachate, contaminant or precious metals laden fluids, water, and more) into the environment. Impermeable/low permeability systems are also needed to prevent the infiltration of fluids into materials that need to be covered from the elements – for example waste rock piles that could leach, and create acid mine drainage, when exposed to water and other atmospheric conditions.
Impermeable/low permeability bases, side slopes and covers may be constructed for impoundments, ponds, and pads on mine sites using locally available native materials, synthetic membranes, or a combination of both native and synthetic materials (in a composite system). The use of native materials can significantly reduce capital costs for construction works, if suitable natural earth materials such as clay or amended soil with bentonite, are locally available to construct compacted low permeability systems. Nonetheless, the lower permeability to fluid flow offered by synthetic membranes and composite systems (compacted clay and synthetic membranes) provides an advantage over the use of compacted clay systems alone. For comparison, the permeability of synthetic membranes may be over six orders of magnitude lower than that of compacted clay – at up to 10-7 m/s for compacted clay vs. 10-13 m/s for synthetic membranes.
Although the capital costs of constructing synthetic liners may be higher than those for compacted clay materials, especially if good quality clay is locally available, the lower permeability provided by synthetic membranes, and other added benefits (see Table 1) – (such as ease of installation and quality assurance, leak location, repairs, maintenance, and more) provide good considerations for any added costs.
Table 1: Compacted Clay Liners (CCL) vs. synthetic membranes as barrier materials (Reference: Daniel and Koerner, 1993 – Cover systems. In: Daniel D.E. (eds) Geotechnical Practice for Waste Disposal)
Aspects considered | Compacted Clay Liners (CCL) | Synthetic membranes |
Desiccation | Susceptible to desiccation from above and below unless protected properly. Designers usually consider drying of the clay layer from the top; however gases and materials in underlying materials may dry out the clay layer from below as well. | Do not desiccate |
Cyclical freezing and thawing, wet and dry cycles | Susceptible to damage from freezing and thawing, wet and dry cycles unless suitably protected | Freezing and thawing, wet and dry cycles do not affect synthetic membranes |
Compaction | Difficult to compact properly on gas collection layers and over soft materials e.g. waste | No need for compaction |
Differential settlement | Differential settlement in the underlying materials may create excessive tensile strains that may cause the CCL to crack | Can withstand large differential settlements. Some are better at it than others |
Repairs | Difficult to repair if they crack | Easier to repair |
Permeability | Several orders of magnitude higher than synthetic membranes (at about 10-7 m/s for CCL vs. 10-13 m/s for synthetic membranes) | Lower permeability to liquids and gases than CCL (permeability can be up to six orders of magnitude lower than CCL – 10-13 m/s for synthetic membranes vs. 10-7 m/s for CCL |
Long term effectiveness as a barrier layer | Because of the higher permeability, potential desiccation, and cracking issues, CCL is considerably not as effective as synthetic membranes for impeding fluid flow long term | Virtually impermeable unless they are damaged. If practices for preventing and finding damages and leaks are incorporated, synthetic membranes are very effective as long term barrier layers |
Construction | Convenient if clay is available locally, may be challenging if clay supply is limited | Readily available and can be shipped to locations. Straight forward and rapid installation. Gas collection penetrations and boots are easy to construct |
Slope stability | May be a concern for steep slopes | Comparatively less concern as they can be anchored and textured for improved slope stability and increased interface friction and shear strength |
The following are some commonly used synthetic membranes, and their suitability and limitations for various mine site conditions and applications
Table 2: Some synthetic membranes for heap leach mining pads, ancillary ponds, processing and storage units (Scheirs, 2009)
Synthetic membrane type | Reasons for suitability | Limitations |
HDPE – High Density Polyethylene |
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LLDPE – Linear Low Density Polyethylene |
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PVC – Polyvinylchloride |
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Hot Solutions Rated Membranes |
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Table 2b presents some surface treatments that may be applied to the surfaces of synthetic membranes to enhance their performance for installation, quality assurance and leak location, interface shear friction and strength.
Table 2b: Some surface treatments that may be applied to synthetic membranes to enhance long term performance
Surface treatments | Reasons for suitability | Limitations |
Conductive coating |
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Light reflective coating to reflect UV light |
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Texturing |
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Table 3 presents some budgetary estimation of costs for the synthetic membranes discussed, including installation costs.
Table 3: Some budgetary costs for synthetic membranes (inclusive of the cost of the synthetic membranes, installation and ancillary costs)
Synthetic membrane type1 | Cost (US$/ft2) (materials and installation) |
HDPE – black – smooth | 1.80 – 1.85 |
LLDPE – black – smooth | 1.80 – 1.85 |
HDPE – Hot Solution Rated | 2.10 – 2.15 |
Conductive – HDPE | 1.85 – 1.90 |
Conductive – LLDPE | 1.85 – 1.90 |
Light reflective surface – HDPE | 1.80 – 1.85 |
Light reflective surface – LLDPE | 1.80 – 1.85 |
Textured – HDPE (medium asperity)2 | 1.85 – 1.90 |
Textured – LLDPE (medium asperity)2 | 1.85 – 1.90 |
PVC | 1.80 – 1.85 |
1 A thickness of 80 mil was used. The cost of the synthetic membranes will increase with the material thickness, since more resin is needed as the thickness increases. The cost of the materials will also vary with the cost of resins and other market conditions (2018 values shown). 2The cost of textured surfaces is dependent on the asperity height following texturing. The cost will increase as the asperity height increases, since more resin is needed for higher asperities.
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References
Daniel D.E., Koerner R.M. (1993) Cover systems. In: Daniel D.E. (eds) Geotechnical Practice for Waste Disposal. Springer, Boston, MA. https://doi.org/10.1007/978-1-4615-3070-1_18
Scheirs, J. 2009. A Guide to Polymeric Geomembranes, 1st Edition, Wiley and Sons, West Sussex, UK