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Radiation occurs naturally throughout the biosphere due to radioactive elements and their decay products present in the earth and through other natural processes. These natural sources expose human beings to radiation both outdoor and indoor. The exposure due to technologically enhanced radiations such as from thermal and nuclear power plants, uranium milling and phosphate fertilizer industries etc. may also contribute significantly. Of all the sources of environmental radiation, radon and its progeny are considered to be responsible for a significant radiation dose to man. Uranium occurs in dispersed state and has a heterogeneous distribution in earth due to the geochemical processes which have slowly recycled the crystal material to and from the earth's mantle. Although considered as the rare element it has higher content in earth's crust than other toxic elements such as K. Sb. Cd, Bi, and Hg. Its concentration varies significantly from rock to rock. It is more abundant in acidic rocks than in basic rocks and is also found in lignite, monazite and phosphate deposits. These rocks come in contact with underground water and uranium is transferred from bed rocks by its leaching action to the water and then to the soil. Human activities like mining and milling are also the chennels for transfer of underlying uranium to surface soil. Radon, a radioactive inert gas having a fairly long half life is the decay product of uranium series and can migrate from the subsoil to indoor and outdoor atmosphere. Building materials may also be the one of the potential sources of indoor radon which causes the build up of radon progeny in dwellings. Now it is well established that higher levels of radon and its progeny pose a health hazard to the general public. Also long term exposure 2 to low levels of radon in dwellings may lead to cause lung cancer. Therefore, the study of uranium levels in various materials, radon and its progeny in dwellings and radon exhalation from building materials is of great importance. Chapter I of the thesis presents a general introduction to naturally occurring radiations, external and internal exposure, technologically enhanced radioactivity, naturally occurring radon, characteristics of radon and its decay products, indoor radon levels, sources of indoor radon, radon exhalation from building materials and relation of radon and its progeny with lung cancer risk. The techniques used for the measurement of radon and its decay products and for the microanalysis of uranium have been discussed in chapter II. Most of the methods detect alpha particles, some y-emissions while a few detect beta decays. Solid State Nuclear Track Detectors (SSNTD's) have been widely used for the measurement of the passive time integrated radon and its progeny, radon exhalation and for microanalyses of uranium. The third chapter of the thesis gives a general idea about SSNTD's, their applications and advantage. The SSNTD's have been extensively used in almost all branches of Nuclear Science and Technology, Health Physics, Environmental science. Earth sciences etc. Different type of track detectors and their relative merits and demerits, various track formation mechanisms and models, track registration criterion, methodologies of track revelation and their visulisation and main applications of etched track detectors have been discussed. 3 The fourth chapter of the thesis depicts the results of the study of radon and its progeny. Indoor radon measurement have been undertaken in about 150 dwellings in hilly regions such as Kohima (Nagaland), Palampur and Baijnath (Himachal Pradesh) and Dehradun (Uttar Pradesh). Kohima, Palampur and Baijnath are supposed to be high background areas. Kohima in Nagaland, the south-eastern region of India is situated at major plateau boundary (Subduction zone). It has mainly sedimentary rocks and is expected to have rich uranium deposits. Palampur and Baijnath in Himachal Pradesh are situated in hills of northern Indian state of Himachal Pradesh which is close to Himalaya. The life style and building construction of these regions are different from the other part of the country. Dehradun is supposed to be a normal background area. Radon measurements have also been carried out in 143 dwellings of Udaipur, Bikaner and Banswara towns situated in Rajasthan province of Northern India. According to Geological Survey of India, these three places fall in pre-cambrian rocks in Aravalli mountain range which can be grouped in Banded Gneissic Comlpex and Aravalli super group. In the Aravalli super group workable phosphorite deposits are present in the significant amount. These phosphorites are invariably associated with dolostones and their P.,G*5 contents vary from 5 to 23%. Trace element analysis indicate higher percentage of natural uranium. Indoor radon measurements were also made in about 150 dwellings of oil refinery area at Mathura and in dwellings in nearby normal background areas of Mathura and Agra towns of the state of Uttar Pradesh. In nature, sedimentary rocks are the sources of oil and gas. There are occasional cases 4 of igneous and metamorphic rocks serving as the source of petroleum. The sedimentary and igneous rocks also contain substantial trace amount of uranium-238 in varying concentrations and in the process of oil exploration, uranium-238 may also be extracted and be present in crude oil and natural gas. Annual effective dose, lung cancer risk and attributable loss of life expectancy have been calculated on the basis of models and compared with the available data for different countries. Fifth chapter of the thesis presents the results of the radon exhalation rate measurements in a large number of soil, fly ash and cement samples. The soil samples were collected from different places of two major Indian states viz. Uttar Pradesh and Rajasthan. Fly ash samples were obtained from the three large thermal power plants operating in our region i.e. Kasimpur, Parichha and Obra. Various brands of cement samples from different manufacturing companies commonly used in constuction activities in the region, were collected from the market. The purpose of the study was to observe the contribution of building materials to radon levels in dwellings. Over the last two decades it has been realised that some materials used for building construction may raise the airborne radioactivity levels in indoor air to unacceptable levels especially when the radium content in the materials is high. Various waste materials produced by power plants, chemical and metallurgical industry are commonly used in building materials. Some of them such as fly ash. furnace slag, byproduct gypsum etc. contain appreciable amount of natural radionuclides from uranium and thorium series and may pose radiation risk to the 5 population. The results of the measurements of the radon exhalation rates with effective dose equivalents, uranium concentration and coefficient of permeability in soil, fly ash and cement samples point out that the uranium concentrations of fly ash samples are much higher than the soil samples but their radon exhalation rates are found to be lower or of the same order. A positive correlation has been found between the radon exhalation rate and the uranium concentration as well as the permeability of these samples. In addition, the radon exhalation rates have been measured in geological samples from the Mosabani copper mine and the Narwapahar and Jaduguda uranium mines areas of the Singhbhum Shear Zone in the state of Bihar, India. The values of radon exhalation rates from crushed rock and soil samples are found to show a positive correlation with the measured values of uranium in the corresponding samples. High values of radon exhalation in subsurface mines like Jaduguda (depth ~ 800m) and Mosabani (depth ~ 1000m) seem to emphasise the need for adequate ventilation for the removal of radon and its progenies from the mining area. In order to study the effect on the radon exhalation rates by adding different amounts of fly ash in the soil, a separate experiment was performed to measure the radon exhalation from intimate mixtures of fly ash and soil samples in different concentrations. From the results gradual decrease in exhalation rate has been observed with the addition of fly ash in soil samples. The last chapter of thesis has been devoted to the microanalysis of uranium in solid phase materials such as soil, fly ash, cement and geological samples from the Mosabani copper mine and the Narwapahar and the 6 Jaduguda uranium mine areas by "fission track registration technique". From the analysis of the samples no significantly high amount of uranium has been observed. But fly ash and rock samples from mining areas have higher levels of uranium and show un-even, uniform and non-uniform distribution.