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    TABLE OF CONTENTS

    INTRODUCTION 1

    URANIUM DEPOSITS 1

    GEOLOGYOF

    URANIUM

    DEPOSITS 1URANIUM RESERVES OF PAKISTAN 2

    BAGHALCHUR 2

    QABULKHEL 4

    MINORU OCCURRENCES 5

    PAKISTAN NUCLEAR ENERGY PROFILE 5

    THE KARACHINUCLEARPOWERPLANT (KANUPP) 5

    CHASHMANUCLEARPOWERPLANT-1(CHASNUPP-1) 6

    CHASHMANUCLEARPOWERPLANT-2(CHASNUPP-2) 6

    PAKISTAN NUCLEAR ENERGY STATISTICS 7

    RADIOACTIVE WASTE DISPOSAL 7

    LOW LEVEL WASTES 8

    INTERMEDIATE LEVEL WASTES 9HIGH LEVEL WASTES 9

    NUCLEAR RELATED FACILITIES IN PAKISTAN 10

    CONCLUSION 10

    REFRENCE 11

    LIST OF FIGURES

    Figure 1: Pakistan, distribution of Tertiary Siwalik Group sediments and location of

    the Baghal Chur and Qabul Khel U deposits (after Moghal 2001) 2

    Figure 2: Dera Ghazi Khan U district, Baghal Chur area, NW-SE cross-sections

    illustrating a the general litho-stratigraphic position of the U-bearing Baghal Chur

    Sand, Dhok Pathan Formation, Middle Siwalik Division; and b the distribution of

    U lenses in the Baghal Chur Sand (after Moghal 1974) 3

    Figure 3: Bannu Basin, Qabul Khel deposit, NE-SW cross-sections along drill fences

    0 (a) and 10 (b) showing the irregular shape of the main ore body in Qabul Khel

    Sandstone and its relationship to the Qabul Khel Shale Horizon and the watertable (after a Moghal 2001; b Mansoor et al. 2002) 4

    Figure4.(A)Source: CANDU http://www.candu.org/paec.html Image @ digital

    Globe,(B) Source: Google Earth Imagery date, February 1, 2005- February 7,

    2008 6

    Figure 5. (A) Source: CNNC China Zhongyuan Engineering (B) Source: Google

    Earth, Image @ Global Eye 6

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    1

    INTRODUCTION

    The countries with no fossil fuels constructing nuclear power stations presently 125

    nuclear power stations are in planning or construction stage. This will result in steady

    increase in uranium demand over the coming centuries.

    Research continues apace to develop commercial nuclear fusion of hydrogen isotopeswhich can be harness for power generation nuclear fission, no matter the type of

    reactor requires supplies of radioactive isotopes 255U which makes up to 0.5% of

    natural uranium. If we bring fast breeder reacts on stream install safety procedure that

    will restore public confidence in nuclear reactor and develop safe solution for nuclear

    waste storage and disposed.

    URANIUM DEPOSITS

    These are of various types covering metallicferrious deposits.

    GEOLOGY OF URANIUM DEPOSITS

    Uranium occurs in a number of different igneous, hydrothermal and sedimentary

    geological environments.

    1. Unconformity related deposits

    2. Sandstone related deposits

    3. Quartz pebble conglomerate deposits

    4. Breccia complex deposits

    5. Vein deposits

    6. Volcanic and caldera related deposits

    7. Surficial deposits

    8. Metsomatic deposits

    9. Collapse breccia pipe deposit

    10. Lignite deposits

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    2

    URANIUM RESERVES OF PAKISTAN

    Uranium deposits and notable occurrences are reported from the Dera Ghazi Khan

    District, Sulaiman Range, Bannu Basin, and Issa Khel, Mianwali District, in

    central Pakistan, and from the Kirthar Range in south Pakistan.

    A number of radioactive localities associated with alkaline igneous rocks, pegmatites,and schists have been discovered in the mountainous northern part of Pakistan.

    Pakistans former U production was essentially concentrated in the Dera Ghazi Khan

    District, estimates a cumulative production of 970 t U and discovered in 1959.

    Uranium was found in Siwaliksandstone nearRakhi Munh in the Sulaiman Range.

    Subsequent exploration led to the discovery of about a dozen small U deposits in the

    Dera Ghazi Khan District in the early 1970s. Taunsa, discovered in 2000/2001 in this

    district, was the latest success.

    Figure 1: Pakistan, distribution of Tertiary Siwalik Group sediments and

    location of the Baghal Chur and Qabul Khel U deposits (after Moghal 2001)

    BAGHAL CHUR

    The blanket sandstone-type Baghal Chur deposit lies about 40 km NW of Dera Ghazi

    Khan. Original resources are not published but are assumed to have been on the order

    of a few hundred tonnes U at grades of 0.05% U. The deposit was mined from 1971 to

    1999 by conventional methods and is depleted.

    Geological Setting

    Baghal Chur is situated in the asymmetrical Baghal Chur syncline; that hosts all U

    deposit. Host rocks are fluvial lacustrine sediments of the Dhok Pathan Formation,

    Mineralization

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    Uranium(-vanadium) mineralization occurs above and below the groundwater table,

    respectively, in oxidized and non-oxidized greywacke in which schist fragments,

    biotite and feldspar predominate. In both environments, mineralization is out of

    equilibrium

    Non-oxidized mineralization: Pitchblende and coffinite are the principal Uminerals in the non-oxidized zone. In addition, uranium is adsorbed by goethite,

    hematite, martite, biotite, clay minerals, and plant remains. Appreciable uranium

    content is also bound in zeolite (clinoptilolite, heulandite) that occurs as discrete

    diagenetic crystals in pore cavities.

    Oxidized mineralization: Tyuyamunite is the principal U mineral but some

    carnotite occurs occasionally. These minerals, in the form of a greenish-yellow

    amorphous powder, coat grains, pebbles, and clay pellets, impregnate the interstices

    between clasts, and locally also associate with crossbeds of heavy minerals. In the

    latter case, bands of yellow U minerals about 1 cm thick follow above or below, or on

    both sides 510 mm thick black, primarily magnetite, heavy mineral bands and cross

    beds.

    Shape and Dimension of Deposits

    The deposit consists of a group of overlapping ore bodies distributed from surface to

    depths of 150200 m. Ore bodies are of strata peneconcordant, elongated to

    amoeba shape.

    Figure 2: Dera Ghazi Khan U district, Baghal Chur area, NW-SE cross-sections

    illustrating a the general litho-stratigraphic position of the U-bearing Baghal Chur

    Sand, Dhok Pathan Formation, Middle Siwalik Division; and b the distribution of U

    lenses in the Baghal Chur Sand (after Moghal 1974)

    BANU BASIN SURGHAR RANGE, NW PAKISTAN

    The Bannu Basin is located in the North-West Frontier Province of Pakistan. It

    contains the small Qabul Khel, Eagle Hill, and Shanawah sandstone U deposits in

    the Surghar Range, an eastern marginal hill range of the basin. U showings hosted by

    Middle Siwalik molasse also occur intermittently over a strike length of 30 km

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    between Kundal and Baggi Qammar in the Khisor Range, a continuation of the

    Surghar Range, south of the Kurram River.

    QABUL KHEL

    Qabul Khel (Kubul Khel), named aft er a small nearby village, is located in the

    southern Surghar Range.. Grades are about 0.05% U. A number of small ore bodies

    were explored in the early 1980s. An experimental underground mining operation was

    carried out initially but ISL mining was finally adopted and a semi-commercial scale

    ISL operation began in mid-1995 on one ore body. Conventional and ISL mining,

    respectively, are hampered by the shape of the ore body, high dip of strata, structural

    complications, poorly cemented rocks, poor solution confinement, influx of a high

    quantity of water, absence of bottom shale at places, high calcium content in water,

    and a water table cover of only 3 m.

    Geological Setting

    The Qabul Khel deposit is located in the plunging, southern part of the Surgharanticline at the eastern margin of the structural Bannu Basin. This basin consists of

    folded molasse of the Siwalik Group. Ore bodies are hosted by the Dhok Pathan

    Formation that forms the upper unit of the Middle Siwalik Division. The Dhok Pathan

    Formation is a cyclic alternating sand-shale sequence that is variably inclined,

    between 20 and 45 SW, in the Qabul Khel area.

    Figure 3: Bannu Basin, Qabul Khel deposit, NE-SW cross-sections along drill fences

    0 (a) and 10 (b) showing the irregular shape of the main ore body in Qabul Khel

    Sandstone and its relationship to the Qabul Khel Shale Horizon and the water table

    (after a Moghal 2001; b Mansoor et al. 2002)

    Mineralization

    Coffinite and pitchblende are the principal U minerals in the unoxidized

    environment below the water table; they occur as pore fillings whereas pitchblende

    also occurs as micro fine globules. Uranophane is typical for the oxidized zone. The

    ore minerals are contained in an assemblage of predominant amphibole, calcite,

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    quartz, mica, and clay minerals. The ore is poorly cemented, largely unconsolidated,

    and fragile

    Shape and Dimensions of Deposits

    The ore body is of irregular tape-like configuration; it has a NW-SE length of some

    200 m, a thickness commonly from 2 to 15 m averaging 6.5 m, persists over a depthinterval from 68 to 118 m below the surface, and averages 0.053% U. The ore

    follows, in NW-SE direction, the trace of the water table at the contact of the Qabul

    Khel Sandstone with underlying\ shale.

    Minor U occurrences

    Kirthar Range, Sind Province, south Pakistan, Shanawah near Karak, KPK, Kallar

    Kahar, Salt Range, central-north Pakistan, Maraghzar Area, north Pakistan.

    PAKISTAN NUCLEAR ENERGY PROFILE

    Pakistans interest in nuclear energy dates back to 1956 when Pakistan AtomicEnergy Commission (PAEC) was established to promote peaceful use of nuclear

    energy in the country.17 Currently, there are two nuclear plants operating under the

    IAEA safeguards, one nuclear reactor is under construction and several reactors are

    proposed to be constructed in the country.

    As of 2012, nuclear powerin Pakistan is provided by 3 licensed-commercial nuclear

    power plants. Pakistan is the first Muslim country in the world to construct and

    operate civil nuclear power plants. The Pakistan Atomic Energy

    Commission (PAEC), the scientific and nucleargovernmental agency, is solely

    responsible for operating these power plants. As of 2012, the electricity generated bycommercial nuclear power plants constitutes roughly ~3.6% of electricity generated in

    Pakistan, compared to ~62% from fossil fuel, ~33% from hydroelectric powerand

    ~0.3% from Coal electricity. Pakistan is one of the fournuclear armed states (along

    with India, Israel, and North Korea) that is not a party to the Nuclear Non-

    Proliferation Treatybut is a member in good standing of the International Atomic

    Energy Agency.

    The Karachi Nuclear Power Plant (KANUPP)

    The Karachi Nuclear Power Plant (KANUPP) is one of the oldest single unit Canada

    Deuterium Uranium (CANDU) Pressurised Heavy Water Reactor (PHWR) with a

    gross capacity of 137 MW, and is owned and operated by PAEC. KANUUP started it

    operation in 1972, and after the completion of its 30 years design life, the Pakistan

    Nuclear Regulatory Authority (PNRA) extended the operational life of this plant at

    reduced capacity. Over the years the safety records of KANUPP have been extremely

    satisfactory as average personal radiation exposures, and release of radioactive

    material are well within the prescribed international limits and standards.

    http://en.wikipedia.org/wiki/Nuclear_powerhttp://en.wikipedia.org/wiki/Pakistanhttp://en.wikipedia.org/wiki/Nuclear_power_plantshttp://en.wikipedia.org/wiki/Nuclear_power_plantshttp://en.wikipedia.org/wiki/Muslim_worldhttp://en.wikipedia.org/wiki/Pakistan_Atomic_Energy_Commissionhttp://en.wikipedia.org/wiki/Pakistan_Atomic_Energy_Commissionhttp://en.wikipedia.org/wiki/Government_of_Pakistanhttp://en.wikipedia.org/wiki/Fossil_fuelhttp://en.wikipedia.org/wiki/Hydroelectric_powerhttp://en.wikipedia.org/wiki/Coal_electricityhttp://en.wikipedia.org/wiki/List_of_states_with_nuclear_weaponshttp://en.wikipedia.org/wiki/Indiahttp://en.wikipedia.org/wiki/Israelhttp://en.wikipedia.org/wiki/North_Koreahttp://en.wikipedia.org/wiki/Nuclear_Non-Proliferation_Treatyhttp://en.wikipedia.org/wiki/Nuclear_Non-Proliferation_Treatyhttp://en.wikipedia.org/wiki/International_Atomic_Energy_Agencyhttp://en.wikipedia.org/wiki/International_Atomic_Energy_Agencyhttp://en.wikipedia.org/wiki/International_Atomic_Energy_Agencyhttp://en.wikipedia.org/wiki/International_Atomic_Energy_Agencyhttp://en.wikipedia.org/wiki/Nuclear_Non-Proliferation_Treatyhttp://en.wikipedia.org/wiki/Nuclear_Non-Proliferation_Treatyhttp://en.wikipedia.org/wiki/North_Koreahttp://en.wikipedia.org/wiki/Israelhttp://en.wikipedia.org/wiki/Indiahttp://en.wikipedia.org/wiki/List_of_states_with_nuclear_weaponshttp://en.wikipedia.org/wiki/Coal_electricityhttp://en.wikipedia.org/wiki/Hydroelectric_powerhttp://en.wikipedia.org/wiki/Fossil_fuelhttp://en.wikipedia.org/wiki/Government_of_Pakistanhttp://en.wikipedia.org/wiki/Pakistan_Atomic_Energy_Commissionhttp://en.wikipedia.org/wiki/Pakistan_Atomic_Energy_Commissionhttp://en.wikipedia.org/wiki/Muslim_worldhttp://en.wikipedia.org/wiki/Nuclear_power_plantshttp://en.wikipedia.org/wiki/Nuclear_power_plantshttp://en.wikipedia.org/wiki/Pakistanhttp://en.wikipedia.org/wiki/Nuclear_power
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    Figure4.(A)Source: CANDU http://www.candu.org/paec.html Image @ digital Globe,(B) Source:Google Earth Imagery date, February 1, 2005- February 7, 2008

    Chashma Nuclear Power Plant-1 (CHASNUPP-1)Chashma Nuclear Power Plant-1 (CHASNUPP-1) is a Pressurized Water Reactor

    (PWR) with a gross capacity of 325 MW (net output of 300 MW) and with a life span

    of 40 years. The construction of CHASNUPP-1 started in 1992 with the help of China

    National Nuclear Cooperation (CNNC). The CHASNUPP is owned and operated by

    PAEC, Safety and security was the most important consideration during its design and

    construction and it became operational in September 2000.22 The PNRA regulates the

    plant by ensuring quality and safety of its operation.

    Figure 5. (A) Source: CNNC China Zhongyuan Engineering (B) Source: Google Earth, Image @Global Eye

    Chashma Nuclear Power Plant-2 (CHASNUPP-2)

    Chashma Nuclear Power Plant-2 (CHASNUPP-2); In December 2005, Pakistan-

    China collaboration undertook the construction of PWR CHASNUPP-2 with a net

    capacity of 300MW. It is reported to cost PKR 51.46 billion (US $ 860 million, with

    $350 million of this financed by China). A safeguard agreement with the IAEA was

    signed in 2006 and grid connection is expected in 2011. Although the total share of

    nuclear energy is very small, but it proves that Pakistan has over 38 years of safe

    operational experience in the field of nuclear power generation. The total installedcapacity of nuclear power plants, as on June 30, 2010, in the country was 462 MW as

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    against the total installed electricity generation capacity of 21593 MW, which

    constitutes a share of nuclear power plant to the total installed generation capacity as

    2.14%.24 The electricity generated through nuclear power plant was increased by

    79.48% during 2009-10. The share of electricity generated through nuclear power

    plants in the country, during 2009-10, was recorded as 2667 GWh (2.68%) as against1486 GWh (1.57%) in the preceding year.

    PAKISTAN NUCLEAR ENERGY STATISTICS

    RADIOACTIVE WASTE DISPOSAL

    The problem arises because radioactive waste convert be neutralized. Other chemicals

    waste or disposal. They are greatly harmful to human. The general public because

    their harmful indeed some time poisonous effects are invisible and cannot be detected

    by human scene.

    CATEGORIES OF RADIOACTIVE WASTES

    There are many different jurisdictions that classify radioactive wastes in

    different categories and to control these different types of wastes by different ways.

    Mostly the radioactive wastes are of such type, which are combination of many

    isotopes. These types contain both short lived and long lived isotopes. On the basis ofwhat the radioactive wastes are differentiated is the amount o radioactive material

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    present not on the basis of time after which the radioactivity is expected to decay

    away to background value. Radionuclide with half lives longer than 30 years are

    regarded as long live wastes and those with half lives less than 30 years are termed as

    short live wastes. The intermediate wastes, those contains significant amount of

    radioactive material relative to low level wastes. On the basis of amount ofradioactive isotopes present, the radioactive wastes are divided into three main

    categories are:

    1. Low level wastes have radioactivity up to 1000 time which is acceptable inenvironment.

    2. Intermediate level wastes have radioactivity between 1000 and 1000000.3. High level wastes have even greater radioactivity.

    Mostly -these wastes emit alpha particles, beta particles and gamma rays. All

    these particles and rays can damage human tissues. All these particles and rays have

    great speed and energy, so to stop these particles and rays many thin sheets of air and

    other materials are required, for alpha particles a few meter of air is required ,for beta

    particle a thin sheet of metal or a few meter of air, to obsorb the gamma rays , a lead

    shielding of several centimeter is required.

    The solid wastes generated by different power plants are always the bulk of

    low level wastes, not much contains by high level wastes. Low level wastes generates

    2000 cubic meter, intermediate generates 100 cubic meter and high level wastes 2

    cubic meter. When a power plant of 1MW operates for one year continuously. A very

    approximate indication of the relative volumes of the major classes of waste from the

    commercial nuclear cycle. Only the High Level fraction of these wastes may require

    consideration for very long-term management.

    Low level wastes

    Those types of wastes which generally contain short lived radioactive

    materials which are hazardous for humans and others. These sources of these wastes

    are various nuclear and industrial activities that use the isotopes to get radiations.

    These wastes are generally generated during mining. The low level radioactive waste

    includes protective shoe covers and clothing, wiping rags, mops, filters, reactor water

    treatment residues, equipment and tools, luminous dials, medical tubes, swabs,

    injection needles, syringes, and laboratory animal carcasses and tissues. The danger of

    exposure to radiation in low-level radioactive waste varies widely according to thetypes and concentration of radioactive material contained in the waste. Low level

    waste containing some radioactive materials used in medical research, processing

    water at a reactor, on the other hand, could lead to death or an increased risk of

    cancer. If possible, they are usually compacted into as low a volume as possible, as

    disposal costs of these wastes are mostly influenced by volume.

    These may be discarded into normal waste streams after a short period of

    storage time sufficient to allow 'complete' radioactive decay. Longer-term storage

    beyond a few decades, where required, is often into controlled shallow-burial sites

    and enclosed concrete vaults, or even into deep geological disposal locations. For

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    example, the short lived radioactive waste Zr-95, may require management for as little

    as about 30 years. Some elements half life and hazard life is:

    Tritium, half-life of 12 years, hazardous life of 120-240 years.

    Strontium-90, half life of 28 years, hazardous life of 280-560 years.

    Iodine-131, half-life of 8 days, hazardous life of 80-160 days.Technetium-99m, half-life of 6 hours, hazardous life of 2.5-5 days.

    Intermediate level wastes

    The waste level which cannot be easily distinguished from the low level and

    high level wastes but differ in their activities and radioactivity. The Intermediate level

    wastes are generated from the used industrial and medical devices and related

    isotopes. Intermediate-level waste contains higher amounts of radioactivity and

    requires shielding. Intermediate-level wastes includes resins, chemical

    sludge and metal reactor nuclear fuel cladding, as well as contaminated materialsfrom reactor decommissioning. When intermediate level wastes are disposed off,

    some enter to high level wastes and other goes into low level wastes. These types of

    wastes are generally stored in special type of containers for disposal at nuclear plant.

    These types of wastes are generally stored in steel drums to prevent leakage before

    being placed into surface storage or shallow or deep burial. It may be solidified

    in concrete orbitumen for disposal.

    High level wastes

    High level wastes contain both short lived and long lived radionuclide. In high

    level wastes, those radioactive materials are present which have sufficientradioactivity and can generates higher amount of heat. To minimize their exposure

    and heating effects over some defined period of time, which depends upon their half

    lives and security, they require sufficient shielding, isolation and specific management

    to control them. They mostly contains spent nuclear fuels and separated fission wastes

    and medical and industrial devices. In the case of spent nuclear fuel, at the initial

    stage they require water for cooling up to about 10 years to remove the heating effects

    caused by the radioactivity. These consist of the small tonnage of spent fuel

    discharged from the reactor. They contain all of the fission products (about 3 percent

    of the wastes) and un-fission actinides (about 97 percent). When uranium fuel hasbeen used in a reactor for a while, it is no longer as efficient in splitting its atoms and

    producing heat to make electricity. It is then called spent nuclear fuel. About one-

    fourth to one-third of the total fuel load is spent and is removed from the reactor every

    12 to 18 months and replaced with fresh fuel.

    http://en.wikipedia.org/wiki/Resinhttp://en.wikipedia.org/wiki/Chemical_sludgehttp://en.wikipedia.org/wiki/Chemical_sludgehttp://en.wikipedia.org/w/index.php?title=Metal_reactor&action=edit&redlink=1http://en.wikipedia.org/wiki/Nuclear_fuelhttp://en.wikipedia.org/wiki/Nuclear_decommissioninghttp://en.wikipedia.org/wiki/Concretehttp://en.wikipedia.org/wiki/Bitumenhttp://en.wikipedia.org/wiki/Bitumenhttp://en.wikipedia.org/wiki/Concretehttp://en.wikipedia.org/wiki/Nuclear_decommissioninghttp://en.wikipedia.org/wiki/Nuclear_fuelhttp://en.wikipedia.org/w/index.php?title=Metal_reactor&action=edit&redlink=1http://en.wikipedia.org/wiki/Chemical_sludgehttp://en.wikipedia.org/wiki/Chemical_sludgehttp://en.wikipedia.org/wiki/Resin
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    Figure 6. Map showing nuclear facilities in Pakistan

    CONCLUSION

    The arguments clearly establish nuclear power is one of the efficient sources of

    energy; and for a developing country like Pakistan, the decision to generate electricity

    through nuclear power will continue to play a dominant role .

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    REFRENCES

    An Introduction to Economic Geology and Its Environmental Impact byAnthony M.

    EvansAzhar et al. 2003; Baig 1990; Basham 1980; Basham and Rice 1974; Mansoor et al.

    2002; Moghal 1974a,b; 1992, 2001; OECD-NEA/IAEA 1997, 1999;

    OECDNEA/ IAEA/IUREP 1978.

    McKay, A., and Miezitis, Y. (2001) Australias Uranium Resources, Geology And

    Development Of Deposits, Geoscience Austrlai

    Nuclear Energy: Prospects for Pakistan by Malik Qasim Mustafa