International Journal of Marine Science 2014, Vol.4, No.35
            
            
              http://ijms.biopublisher.ca
            
            
              2
            
            
              size and heavy mineral distributions regarding its
            
            
              contents of the natural radioactive elements of the Nile
            
            
              Delta coastal sediments has been investigated by
            
            
              El-Gamal and Saleh (2012).
            
            
              The present work aims to assess radioactivity
            
            
              distribution in erosion and accretion sites in Nile Delta
            
            
              Profiles and to indicate this variation in surf, breaker
            
            
              and off shore zones in Nile Delta coastal area and its
            
            
              surrounding environment. The data obtained will be
            
            
              used as reference information to assess any change in
            
            
              radioactivity background levels due to coastal
            
            
              processes such as erosion and accretion or any
            
            
              influences on the radiation environment. These results
            
            
              can guide us to a better understanding of
            
            
              oceanographic and coastal processes and phenomena
            
            
              in order to protect and for management of the marine
            
            
              environment.
            
            
              1 Results and Discussions
            
            
              The present study revealed that the sediment samples
            
            
              collected from Nile Delta coastal profiles contain
            
            
              primordial terrestrial radioactive elements at
            
            
              remarkably natural levels. Based on HPGe Detector
            
            
              Gamma spectrometric measurements, it could be
            
            
              inferred that elements such as Uranium (
            
            
              238
            
            
              U),
            
            
              Thorium (
            
            
              232
            
            
              Th) and Potassium (
            
            
              40
            
            
              K) are the major
            
            
              causative factors for the radioactivity thus confirming
            
            
              to the previous observations (Ibrahim et al., 1993;
            
            
              El-Gamal et al., 2004; Saleh et al., 2004; Hussein,
            
            
              2011; El-Gamal and Saleh, 2012). The study indicated
            
            
              that the distribution of the sediment grain size and the
            
            
              natural radioactive nuclides under investigation are
            
            
              dependent on the geological and chemical characters
            
            
              of the coastal sediments and controlled by coastal
            
            
              processing (erosion or accretion) and the protection
            
            
              structure established on the coast.
            
            
              It is well known that, at the erosion sites, parts of the
            
            
              sediments are removed and transported with the main
            
            
              sea current to deposit at the next sites parallel to the
            
            
              shoreline or transported seaward to the next position
            
            
              at the same profile. The depths of the profiles under
            
            
              investigation were compared with the previous depth
            
            
              records of the same profiles to indicate the actual
            
            
              situation of them are either erosion or accretion.
            
            
              Figure 1A shows that West of Rosetta profile was
            
            
              recognized as erosion profile at its sampling sites.
            
            
              Figures 1B and F represent East of Rosetta and East of
            
            
              Ras El-Bar profiles beginning as erosion at distances
            
            
              from 100-300 m and continue as accretion sites at the
            
            
              400-500 m distances. On the other hand, Figure 1D
            
            
              shows East of El-Burullus profile was recognized as
            
            
              accretion profile. Figures 1C and E show that West of
            
            
              El-Burullus and West of Ras El-Bar profiles were
            
            
              started as accretion sites at distances from 100-300 m
            
            
              and continue as erosion sites at the 400-500 m
            
            
              distances.
            
            
              Results of the activity concentrations of primordial
            
            
              radionuclides
            
            
              226
            
            
              Ra,
            
            
              232
            
            
              Th and
            
            
              40
            
            
              K (values reported as
            
            
              Bq/kg) and the ratio
            
            
              226
            
            
              Ra/
            
            
              232
            
            
              Th as well as the
            
            
              calculated radiation hazards indices of the sediment
            
            
              samples are given in Table 1. Out of the 275 km
            
            
              stretch of the coastal line featured in our present study
            
            
              in Nile Delta and coastal profiles extending to 500 m
            
            
              distance, the average activity of
            
            
              226
            
            
              Ra was 23.79±8.54
            
            
              Bq/kg and it found to be the highest value
            
            
              (40.3±6.77Bq/kg) at 400 m distance west of Ras
            
            
              El-Bar, while the lowest activity (10.42±7.92Bq/kg)
            
            
              was recorded at 200 m distance east of Rosetta.
            
            
              Likewise, the average activity of
            
            
              232
            
            
              Th was
            
            
              23.95±11.79 Bq/kg and its highest activity
            
            
              (53.1±10.26 Bq/kg) was recorded at 500 m distance
            
            
              from west of Ras El-Bar, the lowest activity of
            
            
              232
            
            
              Th
            
            
              (9.21±6.18Bq kg
            
            
              −1
            
            
              ) was recorded at 500 m distance of
            
            
              east El-Burullus. The average
            
            
              40
            
            
              K activity was
            
            
              280.93±68.19 Bq/kg and its highest activity
            
            
              (399.04±41.85Bq/kg) was recorded at 400 m distance
            
            
              of east El-Burullus, while the lowest activity
            
            
              (160.55±37.48Bq/kg) was recorded at 200 m distance
            
            
              of west Rosetta.
            
            
              The distributions of the detected radionuclides activity
            
            
              concentrations are presented in Figures 2a, 2b and 2c
            
            
              for
            
            
              226
            
            
              Ra,
            
            
              232
            
            
              Th and
            
            
              40
            
            
              K, respectively. Figure 2a shows
            
            
              that generally the eastern profiles have relatively
            
            
              lower
            
            
              226
            
            
              Ra (originally from the heavy nuclide
            
            
              238
            
            
              U)
            
            
              activities than the western profiles. Moreover, at 400
            
            
              and 500 m distances of the western side profiles at
            
            
              Rosetta and Ras El-Bar observed as higher
            
            
              concentrations than the nearest distances (100-300 m)
            
            
              to shore line. The behavior of the heavy radionuclide
            
            
              232
            
            
              Th is like
            
            
              226
            
            
              Ra as shown in Figure 2b. Reverse
            
            
              behavior has been observed for the light radionuclide
            
            
              40
            
            
              K with distribution shown in Figure 2c. This is may
            
            
              be due to that the western profile sediments are
            
            
              subjected more to causes of erosion such as wave and