Our Mining Process
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OUR MINING PROCESS

 
An open-pit mine is the least expensive of all mining methods, and is every developer’s first choice where an orebody is situated close to surface, is big enough, and has little overburden.

Open-pit mines look simple, but every pit needs to be tailor-made. First and foremost, the pit walls have to stay up, so a rock-mechanics engineer
has to determine a safe slope for the pit. There is also a delicate balance between how much waste rock can be mined in order to gain access to the valuable ore and how deep a pit can be.

The size and location of the first bench of any open-pit mine is critical. It is excavated well into the waste rock surrounding an orebody. And since each successive bench is smaller than the last one taken, the depth to which the pit can be mined is determined by the size and location of the first cut or bench.

The amount of waste rock mined relative to the amount of ore mined is called the stripping ratio. In most cases, this ratio is high for the first bench and decreases steadily with each successive bench. A stripping ratio of 3 to 1 means that during the life of the pit, there will be three times as much waste rock mined as ore. To be profitable, an open-pit mine must be designed so that the cost of mining the waste rock does not exceed the value of the ore.

The main cost advantage of open-pit mining is that the miners can use larger and more power shovels and trucks — the equipment is not restricted by the size of the opening it must work in.

This allows faster production, and the lower cost also permits lower grades of ore to be mined.  Open-pit mining, also known as open-cast mining and open-cut mining, refers to a method of extracting rock or minerals from the earth by their removal from an open pit or borrow.

The term is used to differentiate this form of mining from extractive methods that require tunneling into the earth. Open-pit mines are used when deposits of commercially useful minerals or rock are found near the surface; that is, where the overburden (surface material covering the valuable deposit) is relatively thin or the material of interest is structurally unsuitable for tunneling (as would be the case for sand, cinder, and gravel). For minerals that occur deep below the surface—where the overburden is thick or the mineral occurs as veins in hard rock— underground mining methods extract the valued material.

Open-pit mines that produce building materials and dimension stone are commonly referred to as quarries. People are unlikely to make a distinction between an open-pit mine and other types of open-cast mines,[citation needed] such as quarries, borrows, placers, and strip mines.
Open-pit mines are typically enlarged until either the mineral resource is exhausted, or an increasing ratio of overburden to ore makes further mining uneconomic. When this occurs, the exhausted mines are sometimes converted to landfills for disposal of solid wastes. However, some form of water control is usually required to keep the mine pit from becoming a lake.

Open-pit mines are dug on benches, which describe vertical levels of the hole. These benches are usually on four metre to sixty metre intervals, depending on the size of the machinery that is being used. Many quarries do not use benches, as they are usually shallow.
Most walls of the pit are generally dug on an angle less than vertical, to prevent and minimise damage and danger from rock falls. This depends on how weathered the rocks are, and the type of rock, and also how many structural weaknesses occur within the rocks, such as a fault, shears, joints or foliations.

The walls are stepped. The inclined section of the wall is known as the batter, and the flat part of the step is known as the bench or perm. The steps in the walls help prevent rock falls continuing down the entire face of the wall. In some instances additional ground support is required and rock bolts, cable bolts and shotcrete are used. De-watering bores may be used to relieve water pressure by drilling horizontally into the wall, which is often enough to cause failures in the wall by itself.

A haul road is situated at the side of the pit, forming a ramp up which trucks can drive, carrying ore and waste rock.
Waste rock is piled up at the surface, near the edge of the open pit. This is known as the waste dump. The waste dump is also tiered and stepped, to minimise degradation.

Ore which has been processed is known as tailings, and is generally a slurry. This is pumped to a tailings dam or settling pond, where the water evaporates. Tailings dams can often be toxic due to the presence of unextracted sulfide minerals, some forms of toxic minerals in the gangue, and often cyanide which is used to treat gold ore via the cyanide leach process.

After mining finishes, the mine area must undergo rehabilitation. Waste dumps are contoured to flatten them out, to further stabilise them. If the ore contains sulfides it is usually covered with a layer of clay to prevent access of rain and oxygen from the air, which can oxidise the sulfides to produce sulfuric acid, a phenomenon known as acid mine drainage. This is then generally covered with soil, and vegetation is planted to help consolidate the material. Eventually this layer will erode, but it is generally hoped that the rate of leaching or acid will be slowed by the cover such that the environment can handle the load of acid and associated heavy metals. There are no long term studies on the success of these covers due to the relatively short time in which large scale open pit mining has existed. It may take hundreds to thousands of years for some waste dumps to become "acid neutral" and stop leaching to the environment. The dumps are usually fenced off to prevent livestock denuding them of vegetation. The open pit is then surrounded with a fence, to prevent access, and it generally eventually fills up with ground water. In arid areas it may not fill due to deep groundwater levels.

Environmental and health issues

 
The large impact of surface mining on the topography, vegetation, and water resources has made it highly controversial.
Surface mining is subject to state and federal reclamation requirements, but adequacy of the requirements is a constant source of contention. Unless reclaimed, surface mining can leave behind large areas of infertile waste rock, as 70% of material excavated is waste.[citation needed]
In the United States, the Surface Mining Control and Reclamation Act of 1977 mandates reclamation of surface coal mines. Reclamation for non-coal mines is regulated by state and local laws, which may vary widely.

3.0 PRINCIPLES OF RECLAMATION

 
The overall objective of a reclamation plan is to produce a landscape that is safe, stable and compatible with the surrounding landscape and final land use. While recognizing that each mine site has unique characteristics, there are principles that are applicable to all surface mining operations and serve as the foundation for planning and implementing reclamation plans for surface coal mines in Nova Scotia.

Best practices in reclamation planning and management

Mining operations are temporary land use activities and should be conducted with understanding and respect for the environment. Use of reclamation planning and environmental management that aims for sustainability is encouraged in all aspects of reclamation planning, design and implementation. Plans must be science-based, comprehensive in scope and mitigate against safety hazards and environmental effects.

Applied principles of ecological restoration A central purpose in reclamation planning should be to promote the ecological integrity of
each site and surrounding landscapes. The application of ecological restoration principles requires that plans are developed consistent with regional or landscape level ecological objectives. At the local scale, this involves an examination of surrounding landscapes, in combination with determining predicted successional trends of vegetation communities appropriate to enhance local and regional ecosystems. At the site level, emphasis is placed
on reclamation techniques such as land-form replication and planting species that will promote site stability and sustainability. Revegetation should use native species that contribute most to the compatibility of the local ecology.

Compatibility in land use, land cover and landscape design Surface mining also has the potential to visually impact natural scenery, open landscape
character and/or the cultural landscape of adjacent lands. Final reclamation plans and designs should ensure that post-mine or sequential land use or land cover objectives are identified, clearly described and compatible with surrounding landscapes. Landscape design and visual impact assessments should be incorporated into the reclamation planning process. After reclamation is completed and the operation closed, the site should
be self sustaining and/or suitable for an identified or predetermined future land use.

Public consultation and Informed decision-making

 
While respecting landowner prerogatives, surface coal mining activities should provide consideration to community priorities, needs and interests. Reclamation projects can provide lasting benefits to local communities and interested stakeholders can provide important information for plans and decisions that determine reclamation objectives and final land use decisions. Communication and consultation among all parties should be
comprehensive, meaningful and timely. Consultation tools can and should include citizen liaison committees and public information sessions.

BACKFILLING

 
Backfilling of surface mines is highly recommended. Otherwise, methods that ensure public and wildlife safety must be identified in the reclamation plan. Backfilling is critical in or near areas populated by humans. If the post-mining land use includes structures located on backfilled excavations, the reclamation plan needs to specify how and when the backfill material is structurally sound and stable.

Considerations related to backfilling include:
• any contaminated materials such as spilled fuel oil, asphalt and solid waste
must be removed from the site and disposed of at an approved facility prior to backfilling
• construction and demolition debris shall not be used as backfill
• the prevention of subsidence in backfilled material
• the estimation of compaction and settling rates and how these will affect