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Proceeding Paper

Distribution of Natural Radionuclides in Ama Fatma Oil Shale, Morocco †

1
Centre National de l’Energie, des Sciences et des Techniques Nucléaires, Rabat 10001, Morocco
2
Engineering and Materials Laboratory (LIMA), Thermostructural Materials, Polymers and Radiochemistry Team (TMPR), Faculty of Sciences Ben M’Sik Casablanca, Hassan II University of Casablanca, Casablanca 20670, Morocco
*
Author to whom correspondence should be addressed.
Presented at the 4th International Electronic Conference on Applied Sciences, 27 October–10 November 2023; Available online: https://asec2023.sciforum.net/.
Eng. Proc. 2023, 56(1), 229; https://doi.org/10.3390/ASEC2023-15981
Published: 14 November 2023
(This article belongs to the Proceedings of The 4th International Electronic Conference on Applied Sciences)

Abstract

:
The present work aims to analyze the distribution of radionuclides naturally occurring in the oil shale of the Ama Fatma coastal zone. For this purpose, using gamma-ray spectrometry, we analyzed the activity concentrations of uranium (U), thorium (Th) series, and potassium-40 (K-40) in oil shale samples retrieved from the study area. The concentrations of U-238 ranged from 45 ± 36 to 194 ± 50 Bq.kg−1 and those of Th-232 fluctuated between 1.48 ± 0.92 and 9.47 ± 1.06 Bq.kg−1. The measured concentrations for Ra-226, Pb-214, and K-40 oscillated between 33 ± 5 and 138 ± 9 Bq.kg−1, 18 ± 1 and 68 ± 3 Bq.kg−1, and between 17 ± 4 and 279 ± 16 Bq.kg−1, respectively. The obtained values variation appears to be related to the deposit nature and assimilation processes of appropriate radionuclides rather than the retrieved samples’ related depth. The analysis of 232Th/238U and 226Ra/238U allowed an understanding of these radionuclides’ behaviors. The ratios 226Ra/238U ranged from 0.56 to 0.74 with a mean value of 0.70 which indicates the existence of disequilibrium in the investigated oil shale samples. This disequilibrium can be attributed to significant differences in the mobility of these radionuclides.

1. Introduction

The primary source of natural radionuclides is attributed to the three decay chains of 235U, 238U, and 232Th, as well as 40K. 232Th has the longest half-life of 1.405 × 1010 years, followed by 238U with a half-life of 4.47 × 109 years, and 235U with a half-life of 7.1 × 108 years. Natural uranium is composed of 99.27% 238U, 0.72% 235U, and 0.0055% 234U [1]. The radionuclides’ activity concentrations and distribution in natural materials represents high interest as they provide useful information on environmental radioactivity [2]. The principal source of external irradiation to the human body is the gamma radiation emitted by naturally occurring radionuclides. The human external exposure to natural radiation doses is related to the geological and geographical conditions as the associated amount of gamma radiation varies from one region to another along the world [3,4]. Due to this heterogeneity, radionuclides appear in diverse levels in rocks in each region around the world [5]. Higher radiation levels are linked to igneous rocks (e.g., granite) as the content of uranium in a rock increases with silica content [6,7]. It is to be noted that some minerals enclose higher levels of natural radionuclides compared to others [8]. Less important radiation levels are associated with sedimentary rocks [9], with the exception of certain phosphate and shale rocks that display a relatively high content of radionuclides [10].
The examination of sedimentary rocks for uranium and thorium isotopes typically involves a somewhat laborious process of radiochemical procedures to separate the heavy radioactive elements, followed by an analysis of the height of alpha pulses [11,12,13,14,15]. It would be desirable to have simpler and faster methods of analysis. One such alternative is gamma ray spectrometric analysis [16,17] which allows for the non-destructive measurement of the natural gamma ray activity of the core, at energies exceeding approximately 1 MeV. In this particular aspect of the natural gamma spectrum, only three nuclides contribute: 40K, 214Bi, and 208Tl. 40K is a radionuclide that has a long lifespan, whereas 214Bi and 208Tl are short-lived daughters in the decay schemes of 238U and 232Th, respectively.
The present study analyzes the radionuclides concentrations naturally occurring in oil shale samples retrieved from the Ama Fatma coastal zone. The study area is situated in the Tarfaya-Boujdour basin, which defines the Atlantic margin area between the towns of Tarfaya and Boujdour. This region is bounded by the Atlantic Ocean on the west and the Republic of Mauritania on the east, as depicted in Figure 1. Located approximately 80 km to the north of the city, this segment commences with a black shale layer exceeding 2 m in thickness [18,19]. The geological characteristics of the study area consist of Marl, a sedimentary rock abundant in organic matter while the mineral composition of the samples mainly comprises calcite, dolomite, and quartz [18].
The objective of this study includes investigating the natural concentrations of radionuclide elements (238U, 235U, 232Th, 226Ra, 214Pb, and 40K) within Ama Fatma oil shale and assessing the disequilibrium of uranium series radionuclides by studying the 232Th/238U, and 226Ra/238U ratios.

2. Materials and Methods

2.1. Sample Collection and Physical Preparation

The oil shale samples under investigation were collected from the Ama Fatma region, located within the coastal basin of Tarfaya-Boujdour in southwest Morocco (Figure 1). The geographical coordinates of the sampling area are X = 28.202 and Y = −11.781 [19]. These samples were collected at different depths, ranging from 24.18 to 26.69 m from the top of the Ama Fatma outcrop, as shown in Table 1. The physical parameters including total carbon, lithological parameters, and mineralogical composition were analyzed and presented in [18,19] as shown in Table 1. The mineralogical composition was measured using X-ray diffractometry while the granulometry was performed using wet Laser Diffraction equipment (Malvern Mastersizer 2000), namely the Hydro 2000G dispersion Unit [18]. The total carbon was determined using the Rock-Eval pyrolysis method [19].
The obtained oil shale samples were ground to a fine powder using an electric grinder. Then, homogenized samples were weighed and stored in a standard specification plastic container. These containers have been carefully sealed and stored for at least four weeks to prevent contamination of the spectrometer and the escape of 222Rn and 220Rn radiogenic gasses to allow radioactive secular equilibrium to be achieved in the decay chains.

2.2. Analytical Methods

The natural radionuclides (238U, 235U, 232Th, 226Ra, 214Pb, and 40K) activity concentrations were measured by high-resolution gamma-ray spectrometry. The detector used is a low background CANBERRA high-purity coaxial germanium (50% efficiency, 1.8 keV resolution), housed in a 10-cm-thick high-purity lead shield. The gamma spectra delivered by the detector are analyzed by Genie 2000 gamma analysis software. A typical gamma-ray spectrum of an oil shale sample recorded with this system is presented in Figure 2. The 234mPa (1001.03 keV) was used to estimate 238U specific activities, while the peak area at 228Ac (911.32 keV) was used to estimate 232Th. For the determination of 235U, 226Ra, 214Pb, and 40K, their most intensive lines at 143.76 keV, 186.21 keV, 351.92 keV and 1460.81 keV represented their activities, respectively. It worth noting that the spectrometry gamma analytical method requires a significant amount of sample compared to other alternative methods (e.g., Alpha spectrometry).

3. Results and Discussions

3.1. Radionuclides Distributions

Table 2 displays the specific activities of 226Ra, 238U, 232Th, 214Pb, 235U, and 40K measured in oil shale samples collected at different depths from the Ama Fatma coastal zone. The activities of 226Ra, 238U, 232Th, 214Pb, 235U, and 40K ranged between 33.4, 45.1 and 193.7 Bq.kg−1, 1.48 and 9.47 Bq.kg−1, 17.8 and 68.2 Bq.kg−1, 4.02 and 4.75 and between 16.9 and 279.2 Bq.kg−1, respectively. The highest values of 226Ra, 238U, and 235U were recorded in S1 (14). The S1 (16) shows the highest value of 232Th and 40K while S1 (10) indicates the highest value of 214Pb. The obtained activities of 238U and 226Ra measured in the Ama Fatma oil shale are greater than the activities recorded in soil samples reported as not contaminated, while the activities of 232Th and 40K are less high compared to values recorded in the abovementioned soil [20]. The high values of uranium found in the Ama Fatma oil shale samples are related to the oil shale and the sedimentary deposits abundant in the organic materials’ abilities to capture redox-sensitive elements, including Re, V, and U, under reductive conditions [10,13]. In comparison with the oil shale of Timahdit [13], the Ama Fatma oil shale shows less important activities mainly 238U, 235U, and 232Th. It was expected that 232Th, 238U, and 40K would demonstrate distinct environmental behavior, given their particular solubility and varying chemical reactivity [21]. The examination of the exemplary curve (Figure 3) indicates that the specific activities of 226Ra, 238U, 232Th, 214Pb, 235U, and 40K in the oil shale deposits are not related to depth and the irregular recorded variation seems to be related to the lithological factors which probably control the radionuclides’ distribution.

3.2. Pearson Correlation Coefficients among Radionuclides, TOC, and Mineralogical Composition

Pearson correlation coefficients between the measured radionuclides, mineralogical composition, and the total carbon (TOC) in the examined oil shale samples are presented in Table 3. All natural radionuclides of the 238U-series (226Ra, 238U, and 214Pb) showed a strong positive correlation with each other, which means that the distribution mechanisms of 226Ra, 238U, and 214Pb within the oil shale are more or less the same. On the other hand, no correlation was found with the 40K, 232Th, and 238U series, revealing distinctively different mechanisms of control of 40K, 238U, and 232Th concentrations in Ama Fatma oil shale. There are positive correlations between the organic matter content and 40K- and 232Th-specific activities. Organic matter is a component of great importance because it tends to form soluble or insoluble complexes with radionuclides, which can migrate throughout the profile or be retained in the soil [22]. Significative positive correlations were found between 232Th and dolomite and clay, which indicate the association of these radionuclides with dolomite and clay. The 226Ra, 238U, and 235U were found to be positively correlated with pyrite, which is in accordance with earlier results for oil shale from the Timhdit area. These correlations could be attributed to the common affinity of these elements for pyrite minerals.

3.3. Study of 232Th/238U and 226Ra/238U Activity Concentration Ratios

The activity concentration ratios 238U/226Ra and 226Ra/238U were carried out to analyze their variations as shown in Table 2.

3.3.1. 232Th/238U

The calculated 232Th/238U ratios ranged from 0.008 to 0.071 with a mean value of 0.03. The values of the 232Th/238U are very low as the oil shale samples have a marine origin. The obtained low ratio values of 232Th/238U suggest that the studied drilling samples were deposited in a reducing environment [23].

3.3.2. 226Ra/238U

If secular equilibrium prevails in the 238U chain, 226Ra/238U will be approximately 1. Thus, any values of 226Ra/238U other than 1 would suggest the existence of disequilibrium. The ratios 226Ra/238U of Ama Fatma oil shale ranged from 0.56 to 0.74 with a mean value of 0.70. Such ratios being lower than 1 indicate the existence of disequilibrium in the oil shale samples under consideration. This disequilibrium can be attributed to significant differences in the mobility of the radionuclides present. Differential ion mobility has been widely discussed in the literature as a potential cause of such disequilibrium [24,25,26].

4. Conclusions

The study allowed analyzation of the activity concentrations of the 238U, 235U, 232Th, 226Ra, 214Pb, and 40K in shale oil samples collected from the coastal zone of Ama Fatma. The results show that the distribution of studied radionuclides varied independently in depth where it appears to be associated with the lithological characteristic of the zone. The analysis of the 232Th/238U and 226Ra/238U allowed an understanding of these radionuclides’ behavior. The ratios 238U/226Ra ranged from 0.56 to 0.74 with a mean value of 0.70 which indicates the existence of disequilibrium in the investigated oil shale samples. This disequilibrium can be attributed to significant differences in the mobility of these radionuclides. This research data can be used as a valuable resource for further related studies and investigations.

Author Contributions

Conceptualization, S.E.A.; methodology, S.E.A.; software, S.E.A.; validation, S.E.A.; investigation, S.E.A.; resources, S.E.A.; data curation, S.E.A. and N.M.; writing—original draft preparation, S.E.A. and N.M.; writing—review and editing, S.E.A., N.M., A.B., A.L., M.B. and S.F. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are contained within the article.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Dragović, S.; Gajić, B.; Dragović, R.; Janković-Mandić, L.; Slavković-Beškoski, L.J.; Mihailović, N.; Momčilović, M.Z.; Ćujić, M. Edaphic factors affecting the vertical distribution of radionuclides in the different soil types of Belgrade, Serbia. J. Environ. Monit. 2012, 14, 127–137. [Google Scholar] [CrossRef] [PubMed]
  2. Belafrites, A. Natural Radioactivity in Geological Samples from Algeria by SSNTD and Gamma-Ray Spectrometry. In Proceedings of the IX Radiation Physics & Protection Conference, Cairo, Egypt, 15–19 November 2008. [Google Scholar]
  3. Anagnostakis, M.J.; Hinis, E.P.; Simopoulos, S.E.; Angelopoulos, M.G. Natural radioactivity mapping of Greek surface soils. Environ. Int. 1996, 22, 3–8. [Google Scholar] [CrossRef]
  4. Shenber, M.A. Measurement of natural radioactivity levels in soil in Tripoli. Appl. Radiat. Isot. 1997, 48, 147–148. [Google Scholar] [CrossRef]
  5. UNSCEAR (UN Scientific Committee on the Effects of Atomic Radiation). Sources and Effects of Ionizing Radiation; United Nations: New York, NY, USA, 2000.
  6. Aydin, I.; Aydoðan, M.S.; Oksum, E.; Koçak, A. An attempt to use aerial gamma-ray spectrometry results in petrochemical assessments of the volcanic and plutonic associations of Central Anatolia (Turkey). Geophys. J. Int. 2006, 167, 1044–1052. [Google Scholar] [CrossRef]
  7. Zhitkov, A.S.; Vertman, E.M. Uranium and Thorium Content of Reference Samples from the Geological Survey of Japan “Igneous Rock Series 1986”. Geostand. Geoanalytical Res. 2006, 30, 107–111. [Google Scholar] [CrossRef]
  8. Ballesteros, L.; Zarza, I.; Ortiz, J.; Serradell, V. Occupational exposure to natural radioactivity in a zircon sand milling plant. J. Environ. Radioact. 2008, 99, 1525–1529. [Google Scholar] [CrossRef] [PubMed]
  9. Xinwei, L.; Xiaolan, Z. 226Ra, 232Th and 40K activities in soils of Cuihua Mountain National Geological Park, China. Environ. Geol. 2008, 56, 353–357. [Google Scholar]
  10. Balbudhe, A.Y.; Vishwa Prasad, K.; Srivastava, S.K.; Padma Savitri, P.; Holkar, H.; Ravi, P.M.; Tripathi, R.M. Studies of natural radionuclides in rock and soil. In Proceedings of the 19th National Symposium on Environment (NSE-19): Climate Change and Its Impact, Kottayam, India, 11–13 December 2014; pp. 179–180. [Google Scholar]
  11. Azouazi, M.; Ouahidi, Y.; Fakhi, S.; Andres, Y.; Abbe, J.C.; Benmansour, M. Natural radioactivity in phosphates, phosphogypsum and natural waters in Morocco. J. Environ. Radioact. 2001, 54, 231–242. [Google Scholar] [CrossRef] [PubMed]
  12. Galindo, C.; Fakhi, S.; Nourreddine, A.; Hannache, H. Radiochemical Methods Analysis of U and Th: Metrological and Geochemical Applications. In Uranium, Mining and Hydrogeology; Springer: Berlin/Heidelberg, Germany, 2008; pp. 799–806. [Google Scholar]
  13. Galindo, C.; Mougin, L.; Nourreddine, A.; Fakhi, S. Study of the partitioning of uranium and thorium in Moroccan black shale. Czechoslov. J. Phys. 2006, 56, D49–D54. [Google Scholar] [CrossRef]
  14. Fakhi, S.; Outayad, R.; Fait, E.; Mouflih, M.; Rentería, M.; Vioque, I.; Idrissi, A.A.; Benmansour, M.; Bouih, A.; Elhadi, H.; et al. Lithofacies Study of the Natural Phosphates: Quantification, Genetic Involvement and Distribution of Natural Radionuclides. In The New Uranium Mining Boom; Merkel, B., Schipek, M., Eds.; Springer: Berlin/Heidelberg, Germany, 2012; pp. 287–296. [Google Scholar] [CrossRef]
  15. Fakhi, S.; Outayad, R.; Fait, E.; Faiz, Z.; Galindo, C.; Bouih, A.; Benmansour, M.; Benkdad, A.; Vioque, I.; Rentaria, M.; et al. Sequential extraction of U and Th isotopes: Study of their intrinsic distribution in phosphate and limestone sedimentary rock in comparison with black shale. In Uranium-Past and Future Challenges: Proceedings of the 7th International Conference on Uranium Mining and Hydrogeology; Springer International Publishing: Cham, Switzerland, 2015; pp. 581–590. [Google Scholar]
  16. Yücel, H.; Solmaz, A.N.; Köse, E.; Bor, D. Spectral interference corrections for the measurement of 238U in materials rich in thorium by a high resolution gamma-ray spectrometry. Appl. Radiat. Isot. 2009, 67, 2049–2056. [Google Scholar] [CrossRef] [PubMed]
  17. Ghadeer, A.; Ibrahim, A.; Al-Masri, M.S. Geochemistry of uranium and thorium in phosphate deposits at the Syrian coastal area (Al-Haffah and Al-Qaradaha) and their environmental impacts. Environ. Geochem. Health 2019, 41, 1861–1873. [Google Scholar] [CrossRef] [PubMed]
  18. El Aouidi, S.; Fakhi, S.; Laissaoui, A.; Malek, O.A.; Benmansour, M.; Ayach, A.; El Batal, Y.; Aadjour, M.; Tahri, M.; El Yahyaoui, A.; et al. Geochemical characterization of the black shale from the Ama Fatma coastal site in the Southwest of Morocco. Am. J. Chem. 2017, 7, 153–162. [Google Scholar]
  19. El Batal, Y. Le potentiel pétrolier du bassin méso-cénozoïque Tarfaya-Boujdour: Caractérisation Sédimentologique, Lithostratigraphique, Géophysique et Géochimique de la Roche Mère d’âge Crétacé Supérieur. Ph.D. Thesis, Hassan II University, Casablanca, Morocco, 2014. [Google Scholar]
  20. Sources and Effects of Ionizing Radiation. UNSCEAR 2008 Report, Volume I: Sources. Scientific Annexes A and B. Available online: https://www.unscear.org/unscear/uploads/documents/unscear-reports/UNSCEAR_2008_Report_Vol.I-CORR.pdf (accessed on 17 July 2023).
  21. Wollenberg, H.A.; Smith, A.R. A geochemical assessment of terrestrial gamma-ray absorbed dose rates. Health Phys. 1990, 58, 183–189. [Google Scholar] [CrossRef] [PubMed]
  22. Khattab, M.R.; Tawfic, A.F.; Omar, A.M. Uranium-series disequilibrium as a tool for tracing uranium accumulation zone in altered granite rocks. J. Environ. Anal. Chem. 2021, 101, 1750–1760. [Google Scholar] [CrossRef]
  23. Ivanovich, M.; Harmon, R.S. Uranium Series Disequilibrium; Application to Environmental Problems; Clarendon Press: Oxford, UK, 1982; pp. 32–39. [Google Scholar]
  24. Baweja, A.S.; Joshi, S.R.; Demayo, A. Radionuclide Content of Some Canadian Surface Waters: A Report on the National Radionuclides Monitoring Program, 1981–1984; Inland Waters Directorate, Environment Canada, Scientific Series; Inland Waters/Lands Directorate, Water Quality Branch: Ottawa, ON, Canada, 1987.
  25. Collerson, K.D.; Gregor, D.J.; McNaughton, D.; Baweja, A.S. Effect of Coal Dewatering and Coal Use on the Water Quality of the East Poplar River, Saskatchewan: A Literature Review; Environment Canada: Regina, SK, Canada, 1991.
  26. Dowdall, M.; O’Dea, J. Ra-226/U-238 disequilibrium in an upland organic soil exhibiting elevated natural radioactivity. J. Environ. Radioact. 2002, 59, 91–104. [Google Scholar] [CrossRef] [PubMed]
Figure 1. A sketched map of the study area showing its main geological features.
Figure 1. A sketched map of the study area showing its main geological features.
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Figure 2. A typical gamma-ray spectrum of oil shale (sample S1(9)).
Figure 2. A typical gamma-ray spectrum of oil shale (sample S1(9)).
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Figure 3. Variation of 226Ra, 238U, 232Th, 214Pb, 235U, and 40K concentrations versus depth.
Figure 3. Variation of 226Ra, 238U, 232Th, 214Pb, 235U, and 40K concentrations versus depth.
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Table 1. Chemical and mineralogical characteristics of Ama Fatma oil shale samples *.
Table 1. Chemical and mineralogical characteristics of Ama Fatma oil shale samples *.
SamplesTOC (%) (Rock Eval) *Depth (m)
(from Top of Outcrop) *
Mineralogical Composition **Lithology *Age *
QuartzCalciteDolomiteClayHaliteFluorapatitePyrite
S1 (9)6.1924.186.870.28.65.57.31.6-Marl very rich in organic matterUpper Cretaceous
S1 (10)5.8424.697.365.38.84.73.19.41.5
S1 (10–13)5.8424.8317.555.814.47.44.40.40.3
S1 (13–14)5.8424.953.467.84.73.75.713.31.7
S1 (14)5.9125.276.766.94.83.92.75.49.7
S1 (15)-25.817.247.920.68.14.10.41.6
S1 (16)7.6426.698.465.114.88.33.3--
** [18], * [19].
Table 2. Specific activities of 226Ra, 238U, 232Th, 214Pb, 235U, and 40K Bq.kg−1 with the respective standard errors (±σ) and isotopic ratios 232Th/238U and 226Ra/238U.
Table 2. Specific activities of 226Ra, 238U, 232Th, 214Pb, 235U, and 40K Bq.kg−1 with the respective standard errors (±σ) and isotopic ratios 232Th/238U and 226Ra/238U.
Samples226Ra±σ238U±σ232Th±σ214Pb±σ235U±σ40K±σ232Th/238U226Ra/238U
S1 (9)104.07.7139.941.72.791.1544.82.34.022.90145.89.00.0200.74
S1 (10)125.08.4172.842.22.440.9068.23.54.402.86110.96.90.0140.72
S1 (10–13)47.75.467.132.64.790.6929.81.64.272.78159.49.20.0710.71
S1 (13–14)33.44.945.136.42.250.8225.01.4--63.65.00.050.74
S1 (14)138.39.2193.750.31.480.9257.73.04.752.8486.46.70.0080.71
S1 (15)40.04.6371.243.3--17.81.1--16.94.2-0.56
S1 (16)131.09.5185.758.59.471.0661.53.24.133.83279.216.20.050.70
Table 3. Pearson correlation coefficients between mineralogy, total organic content, and radionuclides activity concentrations in oil shale samples collected from Ama Fatma, Morocco.
Table 3. Pearson correlation coefficients between mineralogy, total organic content, and radionuclides activity concentrations in oil shale samples collected from Ama Fatma, Morocco.
TOC226Ra238U232Th214Pb235U40KQuartzCalciteDolomiteClayHaliteFluorapatitePyrite
TOC1.00
226Ra0.421.00
238U0.440.991.00
232Th0.900.150.181.00
214Pb0.390.950.940.181.00
235U−0.460.340.36−0.530.301.00
40K0.900.500.480.960.54−0.641.00
Quartz−0.03−0.44−0.380.34−0.48−0.15−0.101.00
calcite0.100.560.49−0.310.59−0.050.34−0.921.00
Dolomite0.58−0.32−0.250.84−0.37−0.630.090.85−0.851.00
Clay0.70−0.17−0.110.91−0.22−0.650.410.75−0.670.941.00
Halite−0.18−0.42−0.47−0.21−0.46−0.71−0.09−0.170.25−0.15−0.121.00
Fluorapatite−0.490.070.03−0.580.260.51−0.22−0.780.56−0.70−0.81−0.091.00
Pyrite0.990.680.70−0.700.460.99−0.13−0.400.43−0.51−0.51−0.600.051.00
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MDPI and ACS Style

El Aouidi, S.; Mejjad, N.; Benkdad, A.; Laissaoui, A.; Benmansour, M.; Fakhi, S. Distribution of Natural Radionuclides in Ama Fatma Oil Shale, Morocco. Eng. Proc. 2023, 56, 229. https://doi.org/10.3390/ASEC2023-15981

AMA Style

El Aouidi S, Mejjad N, Benkdad A, Laissaoui A, Benmansour M, Fakhi S. Distribution of Natural Radionuclides in Ama Fatma Oil Shale, Morocco. Engineering Proceedings. 2023; 56(1):229. https://doi.org/10.3390/ASEC2023-15981

Chicago/Turabian Style

El Aouidi, Samira, Nezha Mejjad, Azzouz Benkdad, Abdelmourhit Laissaoui, Moncef Benmansour, and Said Fakhi. 2023. "Distribution of Natural Radionuclides in Ama Fatma Oil Shale, Morocco" Engineering Proceedings 56, no. 1: 229. https://doi.org/10.3390/ASEC2023-15981

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