Environmental impact of nuclear power
The greenhouse gas emissions from nuclear fission power are much smaller than those associated with coal, oil and gas, and the routine health risks are much smaller than those associated with coal. However, there is a "catastrophic risk" potential if containment fails, which in nuclear reactors can be brought about by overheated fuels melting and releasing large quantities of fission products into the environment. This potential risk could wipe out the benefits. The most long-lived radioactive wastes, including spent nuclear fuel, must be contained and isolated from the environment for a long period of time. On the other side, spent nuclear fuel could be reused, yielding even more energy, and reducing the amount of waste to be contained. The public has been made sensitive to these risks and there has been considerable public opposition to nuclear power.
The 1979 Three Mile Island accident and 1986 Chernobyl disaster, along with high construction costs, also compounded by delays resulting from a steady schedule of demonstrations, injunctions and political actions, caused by the anti-nuclear opposition, ended the rapid growth of global nuclear power capacity. A release of radioactive materials followed the 2011 Japanese tsunami which damaged the Fukushima I Nuclear Power Plant, resulting in hydrogen gas explosions and partial meltdowns classified as a Level 7 event. The large-scale release of radioactivity resulted in people being evacuated from a 20 km exclusion zone set up around the power plant, similar to the 30 km radius Chernobyl Exclusion Zone still in effect. But published works suggest that the radioactivity levels have lowered enough to now have only a limited impact on wildlife. In Japan, in July 2016, Fukushima Prefecture announced that the number of evacuees following the Great East Japan earthquake events, had fallen below 90,000, in part following the lifting of evacuation orders issued in some municipalities.
The spent nuclear fuel from uranium-235 and plutonium-239 nuclear fission contains a wide variety of carcinogenic radionuclide isotopes such as strontium-90, iodine-131 and caesium-137, and includes some of the most long-lived transuranic elements such as americium-241 and isotopes of plutonium. The most long-lived radioactive wastes, including spent nuclear fuel, are usually managed to be contained and isolated from the environment for a long period of time. Spent nuclear fuel storage is mostly a problem in the United States, following a 1977 President Jimmy Carter prohibition to nuclear fuel recycling. France, Great Britain and Japan, are some of the countries which rejected the repository solution. Spent nuclear fuel is a valuable asset, not simply waste. Disposal of these wastes in engineered facilities, or repositories, located deep underground in suitable geologic formations is seen as the reference solution. The International Panel on Fissile Materials has said:
It is widely accepted that spent nuclear fuel and high-level reprocessing and plutonium wastes require well-designed storage for long periods of time, to minimize releases of the contained radioactivity into the environment. Safeguards are also required to ensure that neither plutonium nor highly enriched uranium is diverted to weapon use. There is general agreement that placing spent nuclear fuel in repositories hundreds of meters below the surface would be safer than indefinite storage of spent fuel on the surface.
Common elements of repositories include the radioactive waste, the containers enclosing the waste, other engineered barriers or seals around the containers, the tunnels housing the containers, and the geologic makeup of the surrounding area.
The ability of natural geologic barriers to isolate radioactive waste is demonstrated by the natural nuclear fission reactors at Oklo, Africa. During their long reaction period about 5.4 tonnes of fission products as well as 1.5 tonnes of plutonium together with other transuranic elements were generated in the uranium ore body. This plutonium and the other transuranics remained immobile until the present day, a span of almost 2 billion years. This is quite remarkable in view of the fact that ground water had ready access to the deposits and they were not in a chemically inert form, such as glass.
Despite a long-standing agreement among many experts that geological disposal can be safe, technologically feasible and environmentally sound, a large part of the general public in many countries remains skeptical. One of the challenges facing the supporters of these efforts is to demonstrate confidently that a repository will contain wastes for so long that any releases that might take place in the future will pose no significant health or environmental risk.
Nuclear reprocessing does not eliminate the need for a repository, but reduces the volume, reduces the long term radiation hazard, and long term heat dissipation capacity needed. Reprocessing does not eliminate the political and community challenges to repository siting.
The countries that have made the most progress towards a repository for high-level radioactive waste have typically started with public consultations and made voluntary siting a necessary condition. This consensus seeking approach is believed to have a greater chance of success than top-down modes of decision making, but the process is necessarily slow, and there is "inadequate experience around the world to know if it will succeed in all existing and aspiring nuclear nations". Moreover, most communities do not want to host a nuclear waste repository as they are "concerned about their community becoming a de facto site for waste for thousands of years, the health and environmental consequences of an accident, and lower property values".
In a 2010 Presidential Memorandum, U.S. President Obama established the "Blue Ribbon Commission on America’s Nuclear Future". The Commission, composed of fifteen members, conducted an extensive two-year study of nuclear waste disposal. During their research the Commission visited Finland, France, Japan, Russia, Sweden, and the UK, and in 2012, the Commission submitted its final report. The Commission did not issue recommendations for a specific site but rather presented a comprehensive recommendation for disposal strategies. In their final report the Commission put forth seven recommendations for developing a comprehensive strategy to pursue. A major recommendation was that "the United States should undertake an integrated nuclear waste management program that leads to the timely development of one or more permanent deep geological facilities for the safe disposal of spent fuel and high-level nuclear waste".
Moderate amounts of low-level waste are through chemical and volume control system (CVCS). This includes gas, liquid, and solid waste produced through the process of purifying the water through evaporation. Liquid waste is reprocessed continuously, and gas waste is filtered, compressed, stored to allow decay, diluted, and then discharged. The rate at which this is allowed is regulated and studies must prove that such discharge does not violate dose limits to a member of the public (see radioactive effluent emissions).
Solid waste can be disposed of simply by placing it where it will not be disturbed for a few years. There are three low-level waste disposal sites in the United States in South Carolina, Utah, and Washington. Solid waste from the CVCS is combined with solid radwaste that comes from handling materials before it is buried off-site.
In the United States environmental groups have said that uranium mining companies are attempting to avoid cleanup costs at disused uranium mine sites. Environmental remediation is required by many states after a mine becomes inactive. Environmental groups have filed legal objections to prevent mining companies from avoiding compulsory cleanups. Uranium mining companies have skirted the cleanup laws by reactivating their mine sites briefly from time-to-time. Letting the mines sites stay contaminated over decades increases the potential risk of radioactive contamination leeching into the ground according to one environmental group, the Information Network for Responsible Mining, which started legal proceedings about March 2013. Among the corporations holding mining companies with such rarely used mines is General Atomics.
Power plant emission
Radioactive gases and effluents
Most commercial nuclear power plants release gaseous and liquid radiological effluents into the environment as a byproduct of the Chemical Volume Control System, which are monitored in the US by the EPA and the NRC. Civilians living within 50 miles (80 km) of a nuclear power plant typically receive about 0.1 μSv per year. For comparison, the average person living at or above sea level receives at least 260 μSv from cosmic radiation.
All reactors in the United States are required by law to have a containment building. The walls of containment buildings are several feet thick and made of concrete and therefore can stop the release of any radiation emitted by the reactor into the environment. If a person is to worry about an energy source that releases large amounts of radiation into the environment, they should worry about coal-fired plants. "The waste produced by coal plants is actually more radioactive than that generated by their nuclear counterparts. In fact, the fly ash emitted by a [coal] power plant—a by-product from burning coal for electricity—carries into the surrounding environment 100 times more radiation than a nuclear power plant producing the same amount of energy." Coal-fired plants are much more hazardous to people’s health than nuclear power plants as they release much more radioactive elements into the environment and subsequently expose people to greater levels of radiation than nuclear plants do. "Estimated radiation doses ingested by people living near the coal plants were equal to or higher than doses for people living around the nuclear facilities. At one extreme, the scientists estimated fly ash radiation in individuals' bones at around 18 millirems (thousandths of a rem, a unit for measuring doses of ionizing radiation) a year. Doses for the two nuclear plants, by contrast, ranged from between three and six millirems for the same period. And when all food was grown in the area, radiation doses were 50 to 200 percent higher around the coal plants."
The total amount of radioactivity released through this method depends on the power plant, the regulatory requirements, and the plant's performance. Atmospheric dispersion models combined with pathway models are employed to accurately approximate the dose to a member of the public from the effluents emitted. Effluent monitoring is conducted continuously at the plant.
|California Public Health Goal||14.8|
A leak of radioactive water at Vermont Yankee in 2010, along with similar incidents at more than 20 other US nuclear plants in recent years, has kindled doubts about the reliability, durability, and maintenance of aging nuclear installations in the United States.
Tritium is a radioactive isotope of hydrogen that emits a low-energy beta particle and is usually measured in becquerels (i.e. atoms decaying per second) per liter (Bq/L). Tritium can be contained in water released from a nuclear plant. The primary concern for tritium release is the presence in drinking water, in addition to biological magnification leading to tritium in crops and animals consumed for food.
Tritium, the mass 3 isotope of hydrogen is deliberately created for thermonuclear weapons use, at government-owned reactors like Watts Bar, by irradiating lithium 6 with neutrons to fission i1. Light water reactors, the standard kind in the USA, generate small quantities of deuterium by neutron capture in the water. This consumes enough neutrons that the natural uranium needs enrichment to raise its fissile U-235 content from 0.72% to 3.6% for Pressurised Water Reactors. Canada's CANDU design uses "heavy water", deuterium oxide, and can use un-enriched uranium because deuterium captures so very few of the neutrons. So the rate of production of tritium from the small amount of deuterium in US reactors must be quite low. 18 millilitres (ml) of water contain Avogadro's number of molecules, by definition, which is just over 6 times the 23rd power of 10, in other words 600 thousand million million million. That gives some idea of how small a unit the Becquerel is. A Litre, of course, is a thousand ml.
Legal concentration limits have differed greatly from place to place (see table right). For example, in June 2009 the Ontario Drinking Water Advisory Council recommended lowering the limit from 7,000 Bq/L to 20 Bq/L. According to the NRC, tritium is the least dangerous radionuclide because it emits very weak radiation and leaves the body relatively quickly. The typical human body contains roughly 3,700 Bq of potassium-40. The amount released by any given nuclear plant also varies greatly; the total release for nuclear plants in the United States in 2003 was from nondetected up to 2,080 curies (77 TBq).
Uranium mining is the process of extraction of uranium ore from the ground. The worldwide production of uranium in 2009 amounted to 50,572 tonnes. Kazakhstan, Canada, and Australia are the top three producers and together account for 63% of world uranium production. A prominent use of uranium from mining is as fuel for nuclear power plants. The mining and milling of uranium present significant dangers to the environment.
It follows that, for the same amount of energy, much less uranium needs to be mined than coal, cutting the environmental impacts of uranium mining on nuclear energy generation.
In 2010, 41% of the world's uranium production was produced by in-situ leaching, which uses solutions to dissolve the uranium while leaving the rock in place. The remainder was produced by conventional mining, in which the mined uranium ore is ground to a uniform particle size and then the uranium extracted by chemical leaching. The product is a powder of unenriched uranium, "yellowcake," which is sold on the uranium market as U3O8. Uranium mining can use large amounts of water — for example, the Roxby Downs Olympic Dam mine in South Australia uses 35,000 m³ of water each day and plans to increase this to 150,000 m³ per day.
The Church Rock uranium mill spill occurred in New Mexico on July 16, 1979 when United Nuclear Corporation's Church Rock uranium mill tailings disposal pond breached its dam. Over 1,000 tons of solid radioactive mill waste and 93 millions of gallons of acidic, radioactive tailings solution flowed into the Puerco River, and contaminants traveled 80 miles (130 km) downstream to Navajo County, Arizona and onto the Navajo Nation. The accident released more radiation, although diluted by the 93 million gallons of mostly water and sulfuric acid, than the Three Mile Island accident that occurred four months earlier and was the largest release of radioactive material in U.S. history. Groundwater near the spill was contaminated and the Puerco rendered unusable by local residents, who were not immediately aware of the toxic danger.
Despite efforts made in cleaning up cold war nuclear arms race uranium sites, significant problems stemming from the legacy of uranium development still exist today on the Navajo Nation and in the states of Utah, Colorado, New Mexico, and Arizona. Hundreds of abandoned mines, primarily used for the US arms race and not nuclear energy production, have not been cleaned up and present environmental and health risks in many communities. The Environmental Protection Agency estimates that there are 4000 mines with documented uranium production, and another 15,000 locations with uranium occurrences in 14 western states, most found in the Four Corners area and Wyoming. The Uranium Mill Tailings Radiation Control Act is a United States environmental law that amended the Atomic Energy Act of 1954 and gave the Environmental Protection Agency the authority to establish health and environmental standards for the stabilization, restoration, and disposal of uranium mill waste.
Risk of cancer
Numerous studies have been done on possible effect of nuclear power in causing cancer. Such studies have looked for excess cancers in both plant workers and surrounding populations due to releases during normal operations of nuclear plants and other parts of the nuclear power industry, as well as excess cancers in workers and the public due to accidental releases. There is agreement that excess cancers in both plant workers and the surrounding public have been caused by accidental releases such as the Chernobyl accident. There is also agreement that some workers in other parts of the nuclear fuel cycle, most notably uranium mining – at least in past decades – have had elevated rates of cancer. However, numerous studies of possible cancers caused by nuclear power plants in normal operation have come to opposing conclusions, and the issue is a matter of scientific controversy and ongoing study.
There have been several epidemiological studies that say there is an increased risk of various diseases, especially cancers, among people who live near nuclear facilities. A widely cited 2007 meta-analysis by Baker et al. of 17 research papers was published in the European Journal of Cancer Care. It offered evidence of elevated leukemia rates among children living near 136 nuclear facilities in the United Kingdom, Canada, France, United States, Germany, Japan, and Spain. However this study has been criticized on several grounds – such as combining heterogeneous data (different age groups, sites that were not nuclear power plants, different zone definitions), arbitrary selection of 17 out of 37 individual studies, exclusion of sites with zero observed cases or deaths, etc. Elevated leukemia rates among children were also found in a 2008 German study by Kaatsch et al. that examined residents living near 16 major nuclear power plants in Germany. This study has also been criticised on several grounds. These 2007 and 2008 results are not consistent with many other studies that have tended not to show such associations. The British Committee on Medical Aspects of Radiation in the Environment issued a study in 2011 of children under five living near 13 nuclear power plants in the UK during the period 1969–2004. The committee found that children living near power plants in Britain are no more likely to develop leukemia than those living elsewhere Similarly, a 1991 study for the National Cancer Institute found no excess cancer mortalities in 107 US counties close to nuclear power plants. However, in view of the ongoing controversy, the US Nuclear Regulatory Commission has requested the National Academy of Sciences to oversee a state-of-the-art study of cancer risk in populations near NRC-licensed facilities.
A subculture of frequently undocumented nuclear workers do the dirty, difficult, and potentially dangerous work shunned by regular employees. The World Nuclear Association states that the transient workforce of "nuclear gypsies" – casual workers employed by subcontractors has been "part of the nuclear scene for at least four decades." Existent labor laws protecting worker’s health rights are not properly enforced. A 15-country collaborative cohort study of cancer risks due to exposure to low-dose ionizing radiation, involving 407,391 nuclear industry workers showed significant increase in cancer mortality. The study evaluated 31 types of cancers, primary and secondary.
Nuclear power reactor accidents can result in a variety of radioisotopes being released into the environment. The health impact of each radioisotope depends on a variety of factors. Iodine-131 is potentially an important source of morbidity in accidental discharges because of its prevalence and because it settles on the ground. When iodine-131 is released, it can be inhaled or consumed after it enters the food chain, primarily through contaminated fruits, vegetables, milk, and groundwater. Iodine-131 in the body rapidly accumulates in the thyroid gland, becoming a source of beta radiation.
The 2011 Fukushima Daiichi nuclear disaster, the world's worst nuclear accident since 1986, displaced 50,000 households after radiation leaked into the air, soil and sea. Radiation checks led to bans of some shipments of vegetables and fish.
Production of nuclear power relies on the nuclear fuel cycle, which includes uranium mining and milling. Uranium workers are routinely exposed to low levels of radon decay products and gamma radiation. Risks of leukemia from acute and high doses of gamma radiation are well-known, but there is a debate about risks from lower doses. The risks of other hematological cancers in uranium workers have been examined in very few studies.
Comparison to coal-fired generation
In terms of net radioactive release, the National Council on Radiation Protection and Measurements (NCRP) estimated the average radioactivity per short ton of coal is 17,100 millicuries/4,000,000 tons. With 154 coal plants in the United States, this amounts to emissions of 0.6319 TBq per year for a single plant.
In terms of dose to a human living nearby, it is sometimes cited that coal plants release 100 times the radioactivity of nuclear plants. This comes from NCRP Reports No. 92 and No. 95 which estimated the dose to the population from 1000 MWe coal and nuclear plants at 4.9 man-Sv/year and 0.048 man-Sv/year respectively (a typical Chest x-ray gives a dose of about 0.06 mSv for comparison). The Environmental Protection Agency estimates an added dose of 0.3 µSv per year for living within 50 miles (80 km) of a coal plant and 0.009 milli-rem for a nuclear plant for yearly radiation dose estimation. Nuclear power plants in normal operation emit less radioactivity than coal power plants.
Unlike coal-fired or oil-fired generation, nuclear power generation does not directly produce any sulfur dioxide, nitrogen oxides, or mercury (pollution from fossil fuels is blamed for 24,000 early deaths each year in the U.S. alone). However, as with all energy sources, there is some pollution associated with support activities such as mining, manufacturing and transportation.
A major European Union funded research study known as ExternE, or Externalities of Energy, undertaken over the period of 1995 to 2005 found that the environmental and health costs of nuclear power, per unit of energy delivered, was €0.0019/kWh. This is lower than that of many renewable sources including the environmental impact caused by biomass use and the manufacture of photovoltaic solar panels, and was over thirty times lower than coals impact of €0.06/kWh, or 6 cents/kWh. However the energy source of the lowest external costs associated with it was found to be wind power at €0.0009/kWh, which is an environmental and health impact just under half the price of Nuclear power.
Contrast of radioactive accident emissions with industrial emissions
Proponents argue that the problems of nuclear waste "do not come anywhere close" to approaching the problems of fossil fuel waste. A 2004 article from the BBC states: "The World Health Organization (WHO) says 3 million people are killed worldwide by outdoor air pollution annually from vehicles and industrial emissions, and 1.6 million indoors through using solid fuel." In the U.S. alone, fossil fuel waste kills 20,000 people each year. A coal power plant releases 100 times as much radiation as a nuclear power plant of the same wattage. It is estimated that during 1982, US coal burning released 155 times as much radioactivity into the atmosphere as the Three Mile Island accident. The World Nuclear Association provides a comparison of deaths due to accidents among different forms of energy production. In their life-cycle comparison, deaths per TW-yr of electricity produced from 1970 to 1992 are quoted as 885 for hydropower, 342 for coal, 85 for natural gas, and 8 for nuclear. The figures include uranium mining, which can be a hazardous industry, with many accidents and fatalities.
As with all thermoelectric plants, nuclear power plants need cooling systems. The most common systems for thermal power plants, including nuclear, are:
- Once-through cooling, in which water is drawn from a large body, passes through the cooling system, and then flows back into the water body.
- Cooling pond, in which water is drawn from a pond dedicated to the purpose, passes through the cooling system, then returns to the pond. Examples include the South Texas Nuclear Generating Station.The North Anna Nuclear Generating Station uses a cooling pond or artificial lake, which at the plant discharge canal is often about 30 °F warmer than in the other parts of the lake or in normal lakes (this is cited as an attraction of the area by some residents). The environmental effects on the artificial lakes are often weighted in arguments against construction of new plants, and during droughts have drawn media attention. The Turkey Point Nuclear Generating Station is credited with helping the conservation status of the American Crocodile, largely an effect of the waste heat produced.
- Cooling towers, in which water recirculates through the cooling system until it evaporates from the tower. Examples include the Shearon Harris Nuclear Power Plant.
A 2011 study by the National Renewable Energy Laboratory determined that the median nuclear plant with cooling towers consumed 672 gallons of water per megawatt-hour, less than the median consumption of concentrating solar power (865 gal/MWhr for trough type, and 786 gal/MWhr for power tower type), slightly less than coal (687 gal/MWhr), but more than that for natural gas (198 gal/MWhr). Once-through cooling systems use more water, but less water is lost to evaporation. In the median US nuclear plant with once-through cooling, 44,350 gal/MWhr passes through the cooling system, but only 269 gal/MWhr (less than 1 percent) is consumed by evaporation.
Nuclear plants exchange 60 to 70% of their thermal energy by cycling with a body of water or by evaporating water through a cooling tower. This thermal efficiency is somewhat lower than that of coal-fired power plants, thus creating more waste heat.
It is possible to use waste heat in cogeneration applications such as district heating. The principles of cogeneration and district heating with nuclear power are the same as any other form of thermal power production. One use of nuclear heat generation was with the Ågesta Nuclear Power Plant in Sweden. In Switzerland, the Beznau Nuclear Power Plant provides heat to about 20,000 people. However, district heating with nuclear power plants is less common than with other modes of waste heat generation: because of either siting regulations and/or the NIMBY effect, nuclear stations are generally not built in densely populated areas. Waste heat is more commonly used in industrial applications.
During Europe's 2003 and 2006 heat waves, French, Spanish and German utilities had to secure exemptions from regulations in order to discharge overheated water into the environment. Some nuclear reactors shut down.
Water consumption and risks
During the process of nuclear power generation, large volumes of water are used. The uranium fuel inside reactors undergoes induced nuclear fission which releases great amounts of energy that is used to heat water. The water turns into steam and rotates a turbine, creating electricity. Nuclear plants must collect around 600 gallons/MWh for this process, so the plants are built near bodies of water.
A 2011 study by the National Renewable Energy Laboratory found that nuclear plants with cooling towers consumed 672 gal/MWhr. The water consumption intensity for nuclear was similar to that for coal electricity (687 gal/MWhr), lower than the consumption rates for concentrating solar power (865 gal/MWhr for CSP trough, 786 gal/MWhr for CSP tower), and higher than that of electricity generated by natural gas (198 gal/MWhr).
When intaking water for cooling, nuclear plants, like all thermal power plants including coal, geothermal and biomass power plants, use special structures. Water is often drawn through screens to minimise to entry of debris. The problem is that many aquatic organisms are trapped and killed against the screens, through a process known as impingement. Aquatic organisms small enough to pass through the screens are subject to toxic stress in a process known as entrainment. Billions of marine organisms, such as fish, seals, shellfish, and turtles, essential to the food chain, are sucked into the cooling systems and destroyed.
Greenhouse gas emissions
Many stages of the nuclear fuel chain — mining, milling, transport, fuel fabrication, enrichment, reactor construction, decommissioning and waste management — use fossil fuels, or involve changes to land use, and hence emit carbon dioxide and conventional pollutants. Nuclear energy contributes a very small amount of emissions into the atmosphere which can cause many environmental problems such as global warming. Uranium is not burned in a nuclear power plant as coal is so there are no emissions from it. All of the waste that comes from the fission of uranium stays in the plant and is therefore able to be disposed of in a safe way in which the uranium is kept out of the environment. “About 73 percent of emissions-free electricity in the United States comes from nuclear plants.” Nuclear energy produces far less carbon dioxide than coal, 9 grams per kilowatt hour compared with 790–1017 grams per kilowatt hour for coal. Also, nuclear energy produces the same amount if not less greenhouse gasses than renewable resources. Like all energy sources, various life cycle analysis (LCA) studies have led to a range of estimates on the median value for nuclear power, with most comparisons of carbon dioxide emissions show nuclear power as comparable to renewable energy sources.
To better quantify and compare greenhouse gas emissions reported by researchers using many different assumptions and techniques, the US National Renewable Energy Laboratory is sponsoring meta-analysis studies using harmonization, in which reported life-cycle emissions are adjusted to consistent assumptions. The results commonly narrow the range of carbon emissions for a given energy source. The resulting 2012 study published in the Journal of Industrial Ecology analyzing CO2 life cycle assessment emissions from nuclear power determined that "the collective LCA literature indicates that life cycle GHG emissions from nuclear power are only a fraction of traditional fossil sources and comparable to renewable technologies". It also said that for the most common category of reactors, the light water reactor (LWR): "Harmonization decreased the median estimate for all LWR technology categories so that the medians of BWRs, PWRs, and all LWRs are similar, at approximately 12 g CO2-eq/kWh".
Many commentators have argued that an expansion of nuclear power would help combat climate change. Others have argued that it is one way to reduce emissions, but it comes with its own problems, such as risks related to severe nuclear accidents, war attacks on nuclear sites, nuclear terrorism and currently no generally accepted solution for the disposal of radioactive waste which needs to be heavily guarded for hundreds of thousands of years. These advocates also believe that there are better ways of dealing with climate change than investing in nuclear power, including the improved energy efficiency and greater reliance on decentralized and renewable energy sources.
There is also some uncertainty surrounding the future GHG emissions of nuclear power, which has to do with the potential for a declining uranium ore grade without a corresponding increase in the efficiency of enrichment methods. In a scenario analysis of future global nuclear development, as it could be effected by a decreasing global uranium market of average ore grade, the analysis determined that depending on conditions, median life cycle nuclear power GHG emissions could be between 9 and 110 g CO2-eq/kWh by 2050, with the latter figure regarded as an unrealistic "worst-case scenario" by the authors of the study.
Although this future analyses deals with extrapolations for present Generation II reactor technology, the same paper also summarizes the literature on "FBRs"/Fast Breeder Reactors, of which two are in operation as of 2014 with the newest being the BN-800, for these reactors it states that the "median life cycle GHG emissions ... [are] similar to or lower than [present] LWRs and purports to consume little or no uranium ore.
Environmental effects of accidents and attacks
The worst accidents at nuclear power plants have resulted in severe environmental contamination. However, the extent of the actual damage is still being debated.
Radiation levels at the stricken Fukushima I power plant have varied spiking up to 1,000 mSv/h (millisievert per hour), which is a level that can cause radiation sickness to occur at a later time following a one-hour exposure. Significant release in emissions of radioactive particles took place following hydrogen explosions at three reactors, as technicians tried to pump in seawater to keep the uranium fuel rods cool, and bled radioactive gas from the reactors in order to make room for the seawater.
Concerns about the possibility of a large-scale release of radioactivity resulted in 20 km exclusion zone being set up around the power plant and people within the 20–30 km zone being advised to stay indoors. Later, the UK, France and some other countries told their nationals to consider leaving Tokyo, in response to fears of spreading nuclear contamination. New Scientist has reported that emissions of radioactive iodine and cesium from the crippled Fukushima I nuclear plant have approached levels evident after the Chernobyl disaster in 1986. On March 24, 2011, Japanese officials announced that "radioactive iodine-131 exceeding safety limits for infants had been detected at 18 water-purification plants in Tokyo and five other prefectures". Officials said also that the fallout from the Dai-ichi plant is "hindering search efforts for victims from the March 11 earthquake and tsunami".
According to the Federation of Electric Power Companies of Japan, "by April 27 approximately 55 percent of the fuel in reactor unit 1 had melted, along with 35 percent of the fuel in unit 2, and 30 percent of the fuel in unit 3; and overheated spent fuels in the storage pools of units 3 and 4 probably were also damaged". As of April 2011, water is still being poured into the damaged reactors to cool melting fuel rods. The accident has surpassed the 1979 Three Mile Island accident in seriousness, and is comparable to the 1986 Chernobyl disaster. The Economist reports that the Fukushima disaster is "a bit like three Three Mile Islands in a row, with added damage in the spent-fuel stores", and that there will be ongoing impacts:
Years of clean-up will drag into decades. A permanent exclusion zone could end up stretching beyond the plant’s perimeter. Seriously exposed workers may be at increased risk of cancers for the rest of their lives...
John Price, a former member of the Safety Policy Unit at the UK's National Nuclear Corporation, has said that it "might be 100 years before melting fuel rods can be safely removed from Japan's Fukushima nuclear plant".
In the second half of August 2011, Japanese lawmakers announced that Prime Minister Naoto Kan would likely visit the Fukushima Prefecture to announce that the large contaminated area around the destroyed reactors would be declared uninhabitable, perhaps for decades. Some of the areas in the temporary 12 miles (19 km) radius evacuation zone around Fukushima were found to be heavily contaminated with radionuclides according to a new survey released by the Japanese Ministry of Science and Education. The town of Okuma was reported as being over 25 times above the safe limit of 20 millisieverts per year.
Instead, 5 years later, the government expects to gradually lift the designation of some “difficult-to-return- zones”, a total 337 square kilometres (130 sq mi) area, from around 2021. Rain, wind and natural dissipation have removed radioactive contaminants, lowering levels, like at the central district of Okuma town, to 9 mSv/year, one-fifth the level of five years ago.
As of 2013 the 1986 Chernobyl disaster in the Ukraine was and remains the world's worst nuclear power plant disaster. Estimates of its death toll are controversial and range from 62 to 25,000, with the high projections including deaths that have yet to happen. Peer reviewed publications have generally supported a projected total figure in the low tens of thousands; for example an estimate of 16,000 excess cancer deaths are predicted to occur due to the Chernobyl accident out to the year 2065, whereas, in the same period, several hundred million cancer cases are expected from other causes (from International Agency for Research on Cancer published in the International Journal of Cancer in 2006). The IARC also released a press release stating "To put it in perspective, tobacco smoking will cause several thousand times more cancers in the same population", but also, referring to the numbers of different types of cancers, "The exception is thyroid cancer, which, over ten years ago, was already shown to be increased in the most contaminated regions around the site of the accident". The full version of the World Health Organization health effects report adopted by the United Nations, also published in 2006, included the prediction of, in total, no more of 4,000 deaths from cancer. A paper which the Union of concerned scientists took issue with the report, and they have, following the disputed linear no-threshold model (LNT) model of cancer susceptibility, instead estimated, for the broader population, that the legacy of Chernobyl would be a total of 25,000 excess cancer deaths worldwide. That places the total Chernobyl death toll below that of the worst dam failure accident in history, the Banqiao Dam disaster of 1975 in China.
Large amounts of radioactive contamination were spread across Europe due to the Chernobyl disaster, and cesium and strontium contaminated many agricultural products, livestock and soil. The accident necessitated the evacuation of the entire city of Pripyat and of 300,000 people from Kiev, rendering an area of land unusable to humans for an indeterminate period.
As radioactive materials decay, they release particles that can damage the body and lead to cancer, particularly cesium-137 and iodine-131. In the Chernobyl disaster, releases of cesium-137 contaminated land. Some communities, including the entire city of Pripyat, were abandoned permanently. One news source reported that thousands of people who drank milk contaminated with radioactive iodine developed thyroid cancer. The exclusion zone (approx. 30 km radius around Chernobyl) may have significantly elevated levels of radiation, which is now predominantly due to the decay of cesium-137, for around 10 half-lives of that isotope, which is approximately for 300 years.
Due to the bioaccumulation of cesium-137, some mushrooms as well as wild animals which eat them, e.g. wild boars hunted in Germany and deer in Austria, may have levels which are not considered safe for human consumption. Mandatory radiation testing of sheep in parts of the UK that graze on lands with contaminated peat was lifted in 2012.
In 2007 The Ukrainian government declared much of the Chernobyl Exclusion Zone, almost 490 square kilometres (190 sq mi), a zoological animal reserve. With many species of animals experiencing a population increase since human influence has largely left the region, including an increase in moose, bison and wolf numbers. However other species such as barn swallows and many invertebrates, e.g. spider numbers are below what is suspected. With much controversy amongst biologists over the question of, if in fact Chernobyl is now a wildlife reserve.
The SL-1, or Stationary Low-Power Reactor Number One, was a United States Army experimental nuclear power reactor which underwent a steam explosion and meltdown on January 3, 1961, killing its three operators; John Byrnes, Richard McKinley, and Richard Legg. The direct cause was the improper manual withdrawal of the central control rod, responsible for absorbing neutrons in the reactor core. This caused the reactor power to surge to about 20,000MW and in turn, an explosion occurred. The event is the only known fatal reactor accident in the United States and the first to occur in the world. The accident released about 80 curies (3.0 TBq) of iodine-131, which was not considered significant due to its location in a remote desert of Idaho. About 1,100 curies (41 TBq) of fission products were released into the atmosphere.
Radiation exposure limits prior to the accident were 100 röntgens to save a life and 25 to save valuable property. During the response to the accident, 22 people received doses of 3 to 27 Röntgens full-body exposure. Removal of radioactive waste and disposal of the three bodies eventually exposed 790 people to harmful levels of radiation. The hands of the initial victims were buried separately from their bodies as a necessary measure in response to their radiation levels.
Attacks and sabotage
Nuclear power plants, uranium enrichment plants, fuel fabrication plants, and even potentially uranium mines are vulnerable to attacks which could lead to widespread radioactive contamination. The attack threat is of several general types: commando-like ground-based attacks on equipment which if disabled could lead to a reactor core meltdown or widespread dispersal of radioactivity; and external attacks such as an aircraft crash into a reactor complex, or cyber attacks. Terrorists could target nuclear power plants in an attempt to release radioactive contamination into the environment and community.
- In September 1980, Iran bombed the incomplete Osirak reactor complex in Iraq.
- In June 1981, an Israeli air strike completely destroyed Iraq’s Osirak reactor.
- Between 1984 and 1987, Iraq bombed Iran’s incomplete Bushehr nuclear plant six times.
- In Iraq in 1991, the U.S. bombed three nuclear reactors and an enrichment pilot facility.
The United States 9/11 Commission has said that nuclear power plants were potential targets originally considered for the September 11, 2001 attacks. If terrorist groups could sufficiently damage safety systems to cause a core meltdown at a nuclear power plant, and/or sufficiently damage spent fuel pools, such an attack could lead to a widespread radioactive contamination. According to a 2004 report by the U.S. Congressional Budget Office, "The human, environmental, and economic costs from a successful attack on a nuclear power plant that results in the release of substantial quantities of radioactive material to the environment could be great." An attack on a reactor’s spent fuel pool could also be serious, as these pools are less protected than the reactor core. The release of radioactivity could lead to thousands of near-term deaths and greater numbers of long-term fatalities.
Insider sabotage occurs because insiders can observe and work around security measures. In a study of insider crimes, the authors repeatedly said that successful insider crimes depended on the perpetrators’ observation and knowledge of security vulnerabilities. Since the atomic age began, the U.S. Department of Energy’s nuclear laboratories have been known for widespread violations of security rules. A better understanding of the reality of the insider threat will help to overcome complacency and is critical to getting countries to take stronger preventative measures.
Researchers have emphasized the need to make nuclear facilities extremely safe from sabotage and attacks that could release massive quantities of radioactivity into the environment and community. New reactor designs have features of passive safety, such as the flooding of the reactor core without active intervention by reactor operators. But these safety measures have generally been developed and studied with respect to accidents, not to the deliberate reactor attack by a terrorist group. However, the US Nuclear Regulatory Commission does now requires new reactor license applications to consider security during the design stage.
Following the 2011 Fukushima I nuclear accidents there has been an increased focus on the risks associated with seismic activity and the potential for environmental radioactive release. Genpatsu-shinsai, meaning nuclear power plant earthquake disaster is a term which was coined by Japanese seismologist Professor Katsuhiko Ishibashi in 1997. It describes a domino effect scenario in which a major earthquake causes a severe accident at a nuclear power plant near a major population centre, resulting in an uncontrollable release of radiation in which the radiation levels make damage control and rescue impossible, and earthquake damage severely impedes the evacuation of the population. Ishibashi envisages that such an event would have a global impact seriously affecting future generations.
The 1999 Blayais Nuclear Power Plant flood was a flood that took place on the evening of December 27, 1999. It was caused when a combination of the tide and high winds from the extratropical storm Martin led to the sea walls of the Blayais Nuclear Power Plant in France being overwhelmed. The event resulted in the loss of the plant's off-site power supply and knocked out several safety-related systems, resulting in a Level 2 event on the International Nuclear Event Scale. The incident illustrated the potential for flooding to damage multiple items of equipment throughout a plant, with the potential for radioactive release.
According to Joshua M. Pearce of Michigan Technological University, on a global-scale a “sustainable nuclear power system” would entail: (i) dramatically improving efficient energy use and greenhouse gas emissions intensity by updating technology and functionality through the entire life cycle; (ii) improving nuclear security to reduce nuclear power risks and making sure that the nuclear industry can operate without large public nuclear accident insurance subsidies; (iii) eliminating all radioactive waste at the end of life and minimizing the environmental impact during the nuclear fuel cycle; and (iv) the nuclear industry must regain public trust or face obsolescence, as a diverse range of renewable energy technologies are quickly commercialized. Pearce also believes that the nuclear industry must address the issue of equity, both in the present and for later generations.
Nuclear decommissioning is the process by which a nuclear power plant site is dismantled so that it will no longer require measures for radiation protection. The presence of radioactive material necessitates processes that are occupationally dangerous, and hazardous to the natural environment, expensive, and time-intensive.
Most nuclear plants currently operating in the US were originally designed for a life of about 30–40 years and are licensed to operate for 40 years by the US Nuclear Regulatory Commission. The average age of these reactors is 32 years. Therefore, many reactors are coming to the end of their licensing period. If their licenses are not renewed, the plants must go through a decontamination and decommissioning process. Many experts and engineers have noted there is no danger in these aged facilities, and current plans are to allow nuclear reactors to run for much longer lifespans.
Decommissioning is an administrative and technical process. It includes clean-up of radioactivity and progressive demolition of the plant. Once a facility is fully decommissioned, no danger of a radiologic nature should persist. The costs of decommissioning are to be spread over the lifetime of a facility and saved in a decommissioning fund. After a facility has been completely decommissioned, it is released from regulatory control, and the licensee of the plant will no longer be responsible for its nuclear safety. With some plants the intent is to eventually return to "greenfield" status.
- Anti-nuclear movement
- Church Rock uranium mill spill
- Contesting the Future of Nuclear Power
- Ecological footprint
- Environmental impact of electricity generation
- Greenhouse Solutions with Sustainable Energy
- International Nuclear Event Scale
- List of books about nuclear issues
- Lists of nuclear disasters and radioactive incidents
- Non-Nuclear Futures
- Nuclear or Not?
- Nuclear Power and the Environment
- Plutonium in the environment
- Pro-nuclear movement
- Renewable energy commercialization
- The Clean Tech Revolution
- Three Mile Island accident health effects
- Waste Isolation Pilot Plant
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- Benjamin K. Sovacool. "A Critical Evaluation of Nuclear Power and Renewable Electricity in Asia", Journal of Contemporary Asia, Vol. 40, No. 3, August 2010, p. 373.
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