The environmental impact of iron ore mining in all its phases from excavation to beneficiation to transportation and beyond may have detrimental effects on air quality, water quality, biological species, and nearby communities. [1] [2] [3] This is predominantly a result of large-scale iron ore tailings (solid wastes produced during the beneficiation process of iron ore concentrate) that are released into the environment which are harmful to both animals and humans. [4]
Iron ore is a mixture of rocks and minerals containing enough iron content and sufficient volume and accessibility for mining and transportation to be economically mined. [5] Around five percent of the Earth's crust is composed of iron making it the fourth most abundant element. [6] Globally, iron ore is most commonly found in banded iron formations (BIFs) in the form of magnetite (Fe3O4), hematite (Fe2O3), goethite (FeO(OH)), limonite (FeO(OH)·n(H2O)) or siderite (FeCO3). [7] Hematite and magnetite are the most common types of Iron ore. Roughly 98% of iron ore on the global market is used in iron and steel production. [8] The other 2% of iron ore is used to make powdered iron for certain types of steel, auto parts, and catalysts; radioactive iron for medicine; and iron blue in paints, inks, cosmetics, and plastics. [5] Countries rich in iron ore deposits include Australia, Brazil, Canada, India, China, and South Africa. [6]
Once a fertile site is located, iron ore is typically extracted through open-pit mining. Common extraction methods for iron ore are drilling and blasting. The ore is then transported for processing where it undergoes crushing before being put in a blast furnace where coke smelting converts the iron ore to metallic iron. [9] This is a part of the beneficiation process where the ore is becoming ore concentrate. The gangue minerals become tailings and are transferred to a storage facility.
The high demand for iron necessitates continuous mining and processing, which generates a large amount of solid and liquid waste. Iron ore tailings are leftover materials that are released once mineral processing is complete. [10] This waste includes large amounts of iron and manganese oxides in addition to high pH values. [11] Potentially toxic elements found in iron ore tailings include Ba, Cr, Cd, Co, Cu, Fe, Mn, Pb, Ni, and Zn. [11] It is estimated that nearly 32% of iron ore extracted ends up as tailings. [12] Every year, approximately 1.4 billion tons of iron ore tailings are produced. [6] Iron ore mining sites, as well as the wastewater tailings produced by them, contain high levels of dissolved iron and particulate suspended matter, which alter the water chemistry and metal bioavailability.
After leaving the mine, tailings need to be stored and managed in order to avoid environmental hazards and safety risks. In Brazil, approximately 95% of mining tailings end up in containment dams. [6] Many countries have experienced dam breaks. In 2015, the city of Mariana in Brazil experienced the failure of the Fundão Dam. More than 30 million cubic meters of water and tailings from iron ore mining were released into the environment. [6] Iron ore tailings dam breaks cause serious environmental damage and fatality in humans. Tailings impoundments also have the potential to seep. Seepage can be prevented or at least minimized by creating an impermeable layer. [13] Otherwise, acidic and metal-bearing waters from tailings can affect aquatic habitats and nearby groundwater. [13]
The main sources of emissions during both the construction and operation phases include the products of combustion such as nitrous oxide, carbon dioxide, carbon monoxide, and sulfur dioxide and fugitive dust from the operation of equipment. [14] The main sources of combustion-related emissions during both the construction and operation phases are related to diesel generators, fuel-oil boilers, and on-site road traffic. Fugitive dust emissions can occur during land clearing, ground excavation, and equipment traffic on site. [9] Potential sources of fugitive dust during operation include ore loading and unloading, ore crushing, stockpile erosion, and dust from conveyor systems around the site. [1] [2] [3] Fugitive dust emissions are proportional to the disturbed land area and the level of activity and vary substantially from day to day with varying meteorological conditions. [3] The major effects of industrial air pollution on wildlife include direct mortality, weakening industrial-related injury and disease, and physiological and psychological stress. [15]
Gas and particulate emissions from historical smelting operations have been a source of concern for human health and environmental impacts at some sites. Modern smelters use processes that drastically reduce particulate and sulfur dioxide emissions, recognizing the importance of minimizing and mitigating this impact. Historically, sulfur dioxide was the most common source of concern because it reacts with atmospheric water vapor to form sulfuric acid, also known as acid rain. The acidic conditions that develop in the soils where these emissions precipitate can harm existing vegetation and inhibit the growth of new vegetation. The environmental impact of historical smelting has left barren areas near smelting operations. Some areas that have been impacted for decades are now beginning to recover. Emissions from older metal smelters may have harmed human health in some cases. During the operation of lead-zinc smelters, for example, elevated levels of lead in blood have been measured in residents of some communities located near the smelters. Smelting operations are now combined with environmental controls to prevent potential environmental and health issues related to emissions. [16]
Acid rock drainage is created when water and oxygen interact with sulphur-bearing minerals and chemicals in rocks. [17] Sulphuric acid is the most common chemical reaction that results from mining activities as the beneficiation process requires dissolving the minerals surrounding the ore, which releases metals and chemicals previously bound up in the rock into nearby streams, freshwater bodies, and the atmosphere. [14] [1] [2] [3] Acid is most commonly carried off the mind site by rainwater or surface drainage. [18] Many metals become mobile as water becomes more acidic and at high concentrations these metals become toxic to most life forms. [14] Approaches to preventing and cleaning up acid mine drainage include reclaiming contaminated land, soil removal, direct treatment, filling in abandoned mines, relocating and isolating waste, bacteria control, diverting water, and disposing mine waste underwater. [19]
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Some mines require the draining of nearby wetlands for the beneficiation process and the cooling of project machinery, which affects downstream water quality and water quantity, and flora and fauna. [2] Wetlands include bogs, fens, marsh, swamps, and shallow water. [20] Wetlands serve a number of functional purposes in the biosphere such as collecting and storing surface runoff, moderating stream flows, reducing natural flooding and erosion, cleaning and purifying water, recharging groundwater zones, and providing habitats for plants and animals,. [20] [21] Wetlands are being altered from their natural state to support alternative land uses such as agriculture, urbanization, industrial development, and recreation. [20]
Some animals are more susceptible to change and degradation than others Megafauna, including large mammals such as black bears, caribou, and wolves, have shown notable behavioural changes and is sensitive to noise levels caused by iron ore mining and infrastructure projects shortly before and immediately after the young are born and during the rutting season. [15] [22] [23] These disturbance types increase the distances moved by the animals and may effectively decrease reproductive success and cause starvation. [23] In addition, mining development means new roads and trails are needed for access which greatly impacts wildlife. Animals lose their habitats and are made susceptible to overexploitation, interrupted migration patterns, and lower population sizes. [14] It also affects the abundance of food available for these animals since open-pit mining requires the removal of topsoil and vegetation which diminishes biodiversity. [24]
Water is one of the major natural resources that is being polluted by iron ore mining operations. [25] In order to achieve sustainability, Earth's streams, rivers, lakes, and oceans must remain uncontaminated.
The extraction of iron ore can cause surface runoff and leachate leading to the pollution of nearby water bodies. [26] Iron ore mining pollutes water through metal contamination and heightened sediment levels in streams. [27] The risk of contamination increases when iron ore mining exposes metal-bearing ores rather than exposing ore bodies naturally through erosion and when mined ores are placed on earth surfaces in mineral dressing processes. [28] In the case of Iron Mountain, remediation activities took place in 1990 and water samples taken from seeps came back with negative pH values and were considered the most acidic water ever sampled. [29] Mining can also have an effect on water before the extraction process. During exploration, roads may be poorly built resulting in sedimentation which disrupts water quality. [18] Overall, water quality can be impacted as a result of acid mine drainage, heavy metal contamination and leaching, processing chemicals pollution, and erosion and sedimentation. [18]
The above environmental issues of iron ore mining have disproportionate impacts on Indigenous communities and they remain vulnerable to mining's impacts as a result of their close relationship to the land, water, and other natural resources. [30] According to a study from Spain's Autonomous University of Barcelona, mining has been the cause of 24.7% of environmental conflicts involving Indigenous peoples despite making up only 6.4% of the global population. [31]
Since the excavation and mineral separation process of mining requires the removal of overburden, waste rock, and tailings, the local surface environment, atmosphere, and waterways are greatly affected. [30] In addition, these environmental consequences may persist well after the extractive activities have come to an end. At the landscape scale, deforestation and new infrastructure generate patchy landscapes that can disrupt local wildlife and vegetation patterns. [30] Substantial waste products also contaminate nearby water bodies damaging local fisheries and polluting drinking water. [30] In terms of the local atmosphere, the process of smelting releases toxic smoke and gasses and the production of slag and ash affecting the health of plants, animals, and humans. [30] While the mining industry has been proven to have some positive social and economic impacts, it can also exacerbate already-existing mental health and social issues. Overall, Indigenous land-based livelihoods and traditional ways of life are disproportionately affected making it difficult for them to maintain their identity.
Infrastructure projects must be filed for submission, revision, and assessment under federal or regional legislation to ensure projects are carried out in a sustainable manner if it is thought to have a significant impact on the natural, social, or economic environment. [20] Depending on the size, scope, and scale of particular projects, they can be assessed on a national or regional level. In most countries, larger plans are assessed under federal legislation such as the Canadian Environmental Assessment Act (2012) and smaller projects are reviewed more locally, such as the NL Environmental Protection Act (2010). The purpose of an environmental assessment is to protect the environment and quality of life of the people of the province by facilitating the wise management of the natural resources of the province. [20] The environmental assessment process ensures that projects proceed in an environmentally acceptable manner. [20] The size and scope of iron ore projects make them subject to environmental assessment at all levels of administrative legislation. Since Indigenous populations are especially vulnerable to mining projects, it is expected that they are included in this process and have the ability to participate. Indigenous-led impact assessments (ILIA) allow Indigenous governing bodies to design and conduct this process and evaluate the impacts according to their values, concerns, and priorities. [32] While an ILIA incorporated similar stages to a state-led environmental impact assessment, it differs because it reflects the unique locations, histories, natural resource issues, governance systems, and place-based knowledge of the Indigenous peoples undertaking the assessment. [32]
Old or abandoned mining sites can be dangerous. They may have exposed or hidden entrances to underground workings, as well as old intriguing buildings. [13] Ground sinking, also known as "subsidence," is another safety concern at some mine sites. Where underground workings have come close to the surface, the ground may gradually sink. [13] An unexpected collapse can happen at any moment without notice therefore these areas are usually identified and are best to be avoided. When modern mines close, mine owners mitigate such hazards by sealing off mine workings, regrading and lowering the steep slopes of surface excavations, and salvaging or demolishing buildings and facilities. [13]
Where old mining areas are common, current mine owners, government agencies, or other interested parties may undertake reclamation and safety mitigation projects to address hazards at these sites. [13] These programs serve the purpose of identifying hazards, placing warning and no-trespassing signs, and fencing off dangerous areas. As part of these efforts, entrances to old underground workings may be closed altogether. Some abandoned mine workings have become important bat habitats. Mine openings can be closed to allow bats continued access and protection. [13] This practice is particularly beneficial to endangered bat species. Because many old mine sites may be dangerous, the public is advised to exercise caution and avoid entering them.
The actual mine workings, including open pits and waste rock disposal areas, cause significant physical disturbances at a mine site. Once a mine closes, mining facilities that occupy a small area of the disturbed land can either be salvaged or town down. [13] The main visual and aesthetic impacts of mining are the open pits and waste rock disposal areas. Open-pit mining disturbs larger areas than underground mining making the visual impacts much greater. [13] In addition, the amount of waste rock produced in open pit mines is typically two to three times the amount of ore produced meaning massive amounts of waste rock are removed from the pits and deposited in nearby areas. [13]
While tailings impoundments, leach piles, and slag piles do vary in size, they are generally quite large. [13] Some of the largest mill impoundments, such as those at open pit copper mines, can cover thousands of acres (tens of square kilometres) and be several hundred feet (about 100 meters) thick. [13] Heap leach piles can range in size from a few hundred feet (about 100 m) to hundreds of acres (0.1 to 1 km2). [13]
Mining is the extraction of valuable geological materials and minerals from the surface of the Earth. Mining is required to obtain most materials that cannot be grown through agricultural processes, or feasibly created artificially in a laboratory or factory. Ores recovered by mining include metals, coal, oil shale, gemstones, limestone, chalk, dimension stone, rock salt, potash, gravel, and clay. The ore must be a rock or mineral that contains valuable constituent, can be extracted or mined and sold for profit. Mining in a wider sense includes extraction of any non-renewable resource such as petroleum, natural gas, or even water.
Ore is natural rock or sediment that contains one or more valuable minerals concentrated above background levels, typically containing metals, that can be mined, treated and sold at a profit. The grade of ore refers to the concentration of the desired material it contains. The value of the metals or minerals a rock contains must be weighed against the cost of extraction to determine whether it is of sufficiently high grade to be worth mining and is therefore considered an ore. A complex ore is one containing more than one valuable mineral.
Iron ores are rocks and minerals from which metallic iron can be economically extracted. The ores are usually rich in iron oxides and vary in color from dark grey, bright yellow, or deep purple to rusty red. The iron is usually found in the form of magnetite (Fe
3O
4, 72.4% Fe), hematite (Fe
2O
3, 69.9% Fe), goethite (FeO(OH), 62.9% Fe), limonite (FeO(OH)·n(H2O), 55% Fe), or siderite (FeCO3, 48.2% Fe).
Open-pit mining, also known as open-cast or open-cut mining and in larger contexts mega-mining, is a surface mining technique that extracts rock or minerals from the earth.
Malachite is a copper carbonate hydroxide mineral, with the formula Cu2CO3(OH)2. This opaque, green-banded mineral crystallizes in the monoclinic crystal system, and most often forms botryoidal, fibrous, or stalagmitic masses, in fractures and deep, underground spaces, where the water table and hydrothermal fluids provide the means for chemical precipitation. Individual crystals are rare, but occur as slender to acicular prisms. Pseudomorphs after more tabular or blocky azurite crystals also occur.
In mining, tailings or tails are the materials left over after the process of separating the valuable fraction from the uneconomic fraction (gangue) of an ore. Tailings are different from overburden, which is the waste rock or other material that overlies an ore or mineral body and is displaced during mining without being processed.
Acid mine drainage, acid and metalliferous drainage (AMD), or acid rock drainage (ARD) is the outflow of acidic water from metal mines and coal mines.
Boliden AB is a Swedish multinational metals, mining, and smelting company headquartered in Stockholm. The company produces zinc, copper, lead, nickel, silver, and gold, with operations in Sweden, Finland, Norway, and Ireland.
The Bingham Canyon Mine, more commonly known as Kennecott Copper Mine among locals, is an open-pit mining operation extracting a large porphyry copper deposit southwest of Salt Lake City, Utah, in the Oquirrh Mountains. The mine is the largest human-made excavation, and deepest open-pit mine in the world, which is considered to have produced more copper than any other mine in history – more than 19,000,000 short tons. The mine is owned by Rio Tinto Group, a British-Australian multinational corporation. The copper operations at Bingham Canyon Mine are managed through Kennecott Utah Copper Corporation which operates the mine, a concentrator plant, a smelter, and a refinery. The mine has been in production since 1906, and has resulted in the creation of a pit over 0.75 miles (1,210 m) deep, 2.5 miles (4 km) wide, and covering 1,900 acres. It was designated a National Historic Landmark in 1966 under the name Bingham Canyon Open Pit Copper Mine. The mine experienced a massive landslide in April 2013 and a smaller slide in September 2013.
Silver mining is the extraction of silver by mining. Silver is a precious metal and holds high economic value. Because silver is often found in intimate combination with other metals, its extraction requires the use of complex technologies. In 2008, approximately 25,900 metric tons of silver were consumed worldwide, most of which came from mining. Silver mining has a variety of effects on the environment, humans, and animals.
Iron Mountain Mine, also known as the Richmond Mine at Iron Mountain, is a mine near Redding in Northern California, US. Geologically classified as a "massive sulfide ore deposit", the site was mined for iron, silver, gold, copper, zinc, quartz, and pyrite intermittently from the 1860s until 1963. The mine is the source of extremely acidic mine drainage which also contains large amounts of zinc, copper, and cadmium. One of America's most toxic waste sites, it has been listed as a federal Superfund site since 1983.
The following outline is provided as an overview of and topical guide to mining:
The Climax mine, located in Climax, Colorado, United States, is a major molybdenum mine in Lake and Summit counties, Colorado. Shipments from the mine began in 1915. At its highest output, the Climax mine was the largest molybdenum mine in the world, and for many years it supplied three quarters of the world's supply of molybdenum.
Environmental effects of mining can occur at local, regional, and global scales through direct and indirect mining practices. Mining can cause erosion, sinkholes, loss of biodiversity, or the contamination of soil, groundwater, and surface water by chemicals emitted from mining processes. These processes also affect the atmosphere through carbon emissions which contributes to climate change.
Leviathan Mine is a United States superfund site at an abandoned open-pit sulfur mine located in Alpine County, California. The mine is located on the eastern slope of the Sierra Nevada at about 7,000-foot (2,100 m) elevation, 6 miles (9.7 km) east of Markleeville and 24 miles (39 km) southeast of Lake Tahoe. The mine site comprises approximately 250 acres (100 ha) of land surrounded by the Toiyabe National Forest, which is only accessible a few months a year. The approximately 22 million tons of sulfur ore-containing crushed rock at the mine are responsible for contaminating the Leviathan and Aspen Creek, which join with Mountaineer Creek to form Bryant Creek which ultimately empties into the East Fork of the Carson River. These water bodies are listed as 303(d) impaired. The site location is seismically active.
Rampura Agucha is a zinc and lead mine located on a massive sulfide deposit in the Bhilwara district of Rajasthan, India. Rampura Agucha is located 220 km (140 mi) from Jaipur. It is north of Bhilwara, and northwest of Shahpura. Rampura Agucha is 10 km (6.2 mi) southeast of Gulabpura on NH 79. The mine is owned by Hindustan Zinc Limited (HZL), and has the world's largest deposits of zinc and lead.
A nickel mine is a mine that produces nickel. Some mines produce nickel primarily, while some mines produce nickel as a side-product of some other metal that has a higher concentration in the ore.
The New Idria Mercury Mine encompasses 8,000 acres of land in the Diablo Mountain range, incorporating the town of Idria in San Benito County, California. Idria, initially named New Idria, is situated at 36°25′01″N120°40′24″W and 2440 feet (680m) above mean sea level. The area was, in the past, recorded in the US Census Bureau as a rural community; however, Idria has become a ghost town since the closing of once lucrative mining operations in the early 1970s.
Mount Polley mine is a Canadian gold and copper mine located in British Columbia near the towns of Williams Lake and Likely. It consists of two open-pit sites with an underground mining component and is owned and operated by the Mount Polley Mining Corporation, a wholly owned subsidiary of Imperial Metals. In 2013, the mine produced an output of 38,501,165 pounds (17,463,835 kg) of copper, 45,823 ounces of gold, and 123,999 of silver. The mill commenced operations in 1997 and was closed and placed on care and maintenance in 2019. The company owns 20,113 hectares (201.13 km2) of property near Quesnel Lake and Polley Lake where it has mining leases and operations on 2,007 hectares (20.07 km2) and mineral claims on 18,106 hectares (181.06 km2). Mineral concentrate is delivered by truck to the Port of Vancouver.
Sisson Mine is a proposed tungsten and molybdenum mine which would be sited near the town of Stanley, 60 km North-West of Fredericton, New Brunswick, Canada. The mine would be among the world's largest tungsten mines, with reserves equating to 227 kilotonnes of elemental tungsten (W). The claim owner, Sisson Mines Ltd., proposes to mine 30,000 tonnes per day of ore which contains on average 0.06 per cent tungsten trioxide (WO3) and smaller amounts of molybdenum. The tungsten component of the ore would be refined into an intermediate product ammonium paratungstate (APT) for shipment. Five hundred fifty seven thousand metric ton units (mtu) of APT would be produced per year, which equates to 4,457 tonnes of tungsten metal per year.
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