NUCLEAR WASTE AND REMEDIATION STRATEGY Course Seminar CE 641 - - PowerPoint PPT Presentation

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NUCLEAR WASTE AND REMEDIATION STRATEGY Course Seminar CE 641 - - PowerPoint PPT Presentation

NUCLEAR WASTE AND REMEDIATION STRATEGY Course Seminar CE 641 Presented by Aniruddh Jain Roll No: 09304018 M.Tech 1st Year WHAT IS NUCLEAR ENERGY Nuclear energy is the energy released by the splitting (fission) or merging together (fusion)


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NUCLEAR WASTE AND REMEDIATION STRATEGY

Course Seminar CE 641 Presented by

Aniruddh Jain Roll No: 09304018 M.Tech 1st Year

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WHAT IS NUCLEAR ENERGY ΔE = Δm.c²

In which ΔE = energy release Δm = mass defect c = the speed of light in a vacuum

  • Nuclear energy is the energy released by the splitting (fission)
  • r merging together (fusion) of the nuclei of atom(s).

Nuclear Fusion Nuclear Fission

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NUCLEAR ENERGY FACTS AND FIGURES

On the morning of 6th August,1945 HIROSHIMA

  • A atom bomb named "Little Boy" was dropped at 8:15

am local time

  • Due to the bombing, 90% of the Hiroshima's buildings

were either damaged or completely destroyed.

  • "Practically all living things, human and animal, were

literally seared to death," the Japanese radio broadcaster reported.

  • A fireball with a radius of 200 meters was generated

whose surface temperature reached about 8000 degree centigrade

  • DEATH TOLL 140,000

It contained 64 kg of uranium, of which 0.7 kg underwent nuclear fission, and

  • f this mass only 0.6 g was

transformed into energy. That is with a efficiency of only 1.5 %

Hiroshima before and after

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NUCLEAR ENERGY FACTS AND FIGURES Continued…….

  • On the morning of August 9, 1945 another bomb

“Fat Man” was dropped on the city of Nagasaki

  • Death toll 80,000

Some energy equivalents

  • 1 ton of uranium= 10000 to 16000 tons of oil
  • One kilogram of uranium-235 can theoretically

produce about 20 trillion joules of energy (2 × 1013 joules); as much energy as 1500 tonnes of coal. URANIUM AVAILIBILITY

  • about 40 times as abundant as silver
  • more plentiful than antimony, tin, cadmium,

mercury ,and it is about as abundant as arsenic

  • r molybdenum

NAGASAKI BEFORE & AFTER

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HENCE THE RACE OF POWER AND ENERGY HAS LEAD TO THE DEVELOPEMET OF NUCLEAR ENERGY AND ALONG WITH IT HAS LEAD TO THE GENERATION OF HIGHLY HAZARDOUS NUCLEAR WASTE WHICH HAS POSED A BIG QUESTION OF

NUCLEAR WASTE MANAGEMENT

IN FRONT OF THE DEVELOPED WORLD

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TYPES OF RADIO ACTIVE WASTES

Exempt waste and very low level waste

  • Not harmful to people or the surrounding environment
  • Consist mainly of demolished material (concrete, plaster, bricks, metal etc)

produced during dismantling operations on nuclear industrial sites.

  • Therefore disposed of with domestic refuse

Low level waste

  • Generated from hospitals & industry, as well as the nuclear fuel cycle which

Contains small amounts of mostly short-lived radio activity

  • No shielding required
  • Contains only 1% of radio activity & 90% of volume of total waste

Intermediate level waste

  • Comprises of chemical sludge and metal fuel cladding, contaminated material

from reactor decommissioning

  • Contains 4% of radioactivity & 7% of volume of total waste

High level waste

  • Consists of the fission product & transuranic elements generated in the

reactor core

  • Highly radio active and requires cooling and shielding
  • Contains 95% of the radioactivity & 3% of volume of total waste
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INTERESTING FACT

1000 MW light water reactor

  • Produces 200-350 cubic meter of LLW and ILW
  • 20 cubic meter of HLW

For the same capacity plant

  • 400000 tones of ash is produced
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MANAGING HLW FROM USED FUEL

  • Storage Mostly in ponds at reactor sites

which are usually 7 meter deep to allow 3 meter of water over to fully shield it

  • Some storage is in dry casks of vaults

with air circulation and the fuel is surrounded by concrete which eventually after 40-50 year has one thousand

  • f its original radioactivity. Thus making

handling easy and finally disposing it permanently

  • It also gives a chance to our future

generation to get something out of it.

  • If processed it is vitrified to

borosilicate glass and eventually disposed deep underground

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TREATMENT AND CONDITIONING OF NUCLEAR WASTES

Converting Radioactive waste materials to suitable forms for subsequent management, such as transportation, storage and final disposal Incineration

  • Segregation is done of combustible waste

and then is incinerated at 1000º

  • Resulting ash undergoes cementation or

Bituminization

  • However this technology is subject to

public concern Compaction Volume Reduction technology where that is used mainly for LLW volume reduction Volume reduced upto a factor 5

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TREATMENT AND CONDITIONING OF NUCLEAR WASTES Continued…….

Cementation

  • Solid waste placed into containers is

added with grout and then allowed to set.

  • The monolithic block is suitable for storage

and disposal.

  • Generally used for LLW and ILW
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TREATMENT AND CONDITIONING OF NUCLEAR WASTES Continued…….

Vitrification

  • Nuclear waste here in is incorporated into molten glass (borosilicate)

which is stable and insoluble.

  • Insitu vitrification has also been investigate as a means of “fixing”

activity in contaminated ground as well as creating a barrier to prevent further spread of contamination

  • Use for immobilization of HLW
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STORAGE AND DISPOSAL OPTIONS

Near-surface disposal at ground level, or in caverns below ground level (at depths of tens of meters)

  • Disposal of waste with or without engineering barriers
  • Affected by long term climate changes
  • Hence typically used for LLW & ILW with a radionuclide context of

short half-life( upto about 30 years)

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STORAGE AND DISPOSAL OPTIONS Continued

Deep geological disposal

  • Long time scale of radioactivity
  • f waste led to this idea Isolations

provided by a combination of engineered & natural barriers (rock, salt, clay)

  • A repository is comprised of

mined tunnels or tunnels or caverns into which packaged waste would be placed

  • Some cases (e.g. wet rock)

containers are surrounded by bentonite or cement to provide another barrier

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DEEP GEOLOGICAL DISPOSAL

Methods, Proposed sites & Case Histories Disposal in strong fractured rocks The Swedish proposed disposal concept uses a copper container with a Steel insert to contain the spent fuel. After placement in the repository About 500 m deep in the bedrock the container would be surrounded by a Bentonite clay buffer. Disposal in clay The Belgian disposal concept proposes that spent fuel and HLW is placed in high integrity steel containers and then emplaced in excavated tunnels within a ductile clay. Yucca Mountain Located in the remote Nevada desert, is the proposed site for the Construction of A US national repository to store spent fuel and high-level waste from nuclear power and military defense

  • programmes. The repository would exist 300 meter underground in an

unsaturated layer of volcanic tuff rock. Containment relies on extremely low water table which lies 300m below the repository.

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Yucca Mountain

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DEEP GEOLOGICAL DISPOSAL

Methods & Proposed sites & Case Histories Continued…. Disposal in layered salt strata The Waste Isolation Pilot Plant in New mexico for defence transuranic Waste has been operational since 1999. For this repository natural rock salt is excavated from a several meters thick layer, sandwiched between

  • ther types of rock, 650 below ground level. The wastes placed in these

excavations contain large volumes of long-lived ILW. A feature of salt Environments is the very low rate of groundwater flow and the gradual Self-sealing of the excavations due to creep

  • f the salt.
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OTHER IDEAS FOR DISPOSAL AND WHAT CAN BE THE FUTURE TRENDS

Long-term above ground storage

  • Not currently planned to be implemented

anywhere Disposal in outer space

  • Investigations now abandoned due

to cost and potential risks of launch failure Deep boreholes Deep bore holes drilled from the surface to depths of several kilometers

  • f diameter less than 1m. Containers would be separated from each
  • ther by a layer of bentonite or cement. The top two Km would be

sealed with material such as bentonite , asphalt and concrete. Rock Melting The HLW could be placed in a deep borehole. The heat of the waste can Melt the surrounding rock which on cooling will encase the waste & thus the Waste is distributed throughout the large volume of rock.

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Deep Bore Hole Disposal

Containers release enough heat to create a melt zone around the borehole. As the waste decays and cools, the melt zone resolidifies around the containers, entombing the waste forever.

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Disposal at subduction zone Where one denser section of the Earth’s crust moving towards and Underneath another lighter section. This is marked by an offshore

  • trench. The idea for this option would be to dispose of wastes in the

trench region Such that they would be drawn deep into the Earth. OTHER IDEAS FOR DISPOSAL AND WHAT CAN BE THE FUTURE TRENDS

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Disposal at sea Has been tried in certain countries but this method is not permitted by a number of international agreements. Sub seabed disposal It is been investigated by many countries but not yet implemented. Disposal in ice sheets For this option containers of heat-generating waste would be placed in stable ice sheets such as those found in Greenland and Antarctica. The containers would melt the surrounding ice and be drawn deep into the ice sheet, where the ice would refreeze above the wastes creating a thick barrier. Direct injection Tried in USA and Russia but is not very popular

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NOVEL IDEA

Bioremediation

Some organisms, such as the lichen Trapelia involuta or microorganisms such as the bacterium Citrobacter, can absorb concentrations of uranium that are up to 300 times higher than in their environment.After one day, one gram of bacteria can encrust themselves with nine grams of uranyl phosphate crystals; this creates the possibility that these

  • rganisms could be used in

bioremediation to decontaminate uranium- polluted water. Ref: Wikipidia

COLUMBUS, Ohio, March 17, 2009 (ENS) - An

international team of scientists has found a common soil bacterium that might one day be used to clean up radioactive toxics left from nuclear weapons production decades ago. Ref: Environment News Service (ENS) 2009 The strain Bacillus sphaericus has evolved a crystalline surface layer (S-layer) that covers the

  • utside of the cell. This layer is more than a

protective barrier to the bacteria, it serves to accumulate high amounts of toxic metals such as uranium, lead, copper, aluminum, and cadmium. Bacteria may be the template for new technology aimed at nuclear waste removal. The time may be near when synthetic S-layer discs can be placed in contaminated areas and act as sponges, cleaning up a big toxic mess Ref: Biotechnology Advances. 2005.

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CONCLUSION

NUCLEAR ENERGY IS THE NEED OF FUTURE AND IT WOULD BE FOOLISHNESS ON OUR PART TO HAMPER ITS DEVELOPMENT AND SO IT BECOMES ARE PRIME DUTY TO FIND OUT BETTER WAYS FOR NUCLEAR WASTE MANAGEMENT SO THAT WE CAN BUILD A BETTER FUTURE IN A CLEAN ENVIRONMENT.

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REFRENCES

  • K. Raj , K.K. Prasad, N.K. Bansal 2006, Radioactive waste management

practices in India, Nuclear Engineering and Design Volume 236, Issues 7-8, April, Pages 914-930

  • EPA Handbook Vitrification Technologies for Treatment of Hazardous and

Radioactive Waste, United States Environmental Protection Agency (EPA), EPA/625/R-92/002 (May 1992) available from the EPA's National Service Center for Environmental Publications

  • Classification of Radioactive Waste,A Safety INTERNATIONAL ATOMIC

ENERGY AGENCY, VIENNA, 1994

  • http://www.world-nuclear.org/info/inf04.html
  • http://www.wikipedia.org/
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QUESTIONS ??????