In the eastern Venezuelan Llanos, the drilling fluids composed of wastewater (WW), accompanying hydrocarbons and wastes from oil activity are deposited in a system of waterproofed pits. Later, by means of siphons, the hydrocarbon phase of the WW is separated. WW are typically very salty and contain suspended and dissolved solids, residual hydrocarbons, and chemicals used in hydrocarbon extraction. So they are transported to a pit and treated with a flocculating agent and lime. Once carried out, the flocculation-coagulation operation and pH correction, WW are released to the environment. The savannas where the treated water are irrigated, in addition to the oil operation, present an intense agricultural and livestock activity, and rest on aquifers that are partially replenished with the percolation waters near the treatment pits. Therefore, this research will aim to analyze: i) the levels of soluble salts and heavy metals in the percolation waters collected in lysimeters located in savanna soils adjacent to oil wells after irrigation with WW treated with flocculating agents, and ii) the estimation of time which these salts take to be dislodged from the soil. The waters from the lysimeters did not report high levels of soluble aluminum or heavy metals since their soluble forms were precipitated by liming. Likewise, the coagulation-flocculation process removed the high levels of barium from the untreated WW. The contributions of sodium and calcium from the WW have a liming effect on the acidity of these soils. The sodium levels contributed by the WW could represent an environmental risk, fortunately, the good internal drainage of these sandy Ultisols allows their removal. Studies with lysimeters showed that the percolation waters of areas irrigated with flocculated water have a similar sodium content to that of control lysimeters six months after treatment.
Published in | Journal of Chemical, Environmental and Biological Engineering (Volume 5, Issue 2) |
DOI | 10.11648/j.jcebe.20210502.14 |
Page(s) | 62-68 |
Creative Commons |
This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited. |
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Copyright © The Author(s), 2021. Published by Science Publishing Group |
Sodium, Barium, Aluminum, Contamination, Savannah
[1] | Samanta, S. K., Singh, O. V., and Jain, R. K. (2002). Polycyclic aromatic hydrocarbons: environmental pollution and bioremediation. Trends Biotechnol. 20, 243-248. |
[2] | Konečný F., Boháček, Z., Müller, P., Kovářová, M., and Sedláčková, I. (2003). Contamination of soils and groundwater by petroleum hydrocarbons and volatile organic compounds – Case study: Elslav Brno. Bulletin of Geosciences 78, 225-239. |
[3] | Franco, I., Contin, M., Bragato, G., and De Nobili, M. (2004). Microbiological resilience of soils contaminated with crude oil. Geoderma. 121, 17-30. |
[4] | Asia, I. O., Jegede, S. I., Jegede, D. A., Ize-Iyamu, O. K., and Akpasubi, E. B. (2007). The effects of petroleum exploration and production operations on the heavy metal contents of soil and groundwater in the Niger Delta. International Journal of Physical Sciences. 2 (10), 271-275. |
[5] | López-Hernández, D. (2010). Impacto y resiliencia en indicadores de calidad de suelos en sabanas y morichales de los llanos orientales venezolanos contaminados por un derrame petrolero. In: Contaminación, descontaminación y restauración ambiental en Ibero América. Juan F. Gallardo Lancho (Coord.) Sociedad Ibero Americana de Física y Química Ambiental (SIFQA), Salamanca, España, 165-182. |
[6] | Wokoma, O., and Edori O. (2017). Heavy metals content of an oily wastewater effluent from an oil firm at the point of discharge. International Journal of Chemistry, Pharmacy & Technology, 2 (4), 154-161. |
[7] | Arellano, T. (2008). Manejo integral de fosas de hidrocarburos generadas por la actividad petrolera venezolana. Tesis de Maestría, Universidad de la Fuerza Armada Nacional. Caracas, Venezuela, 119 pp. |
[8] | Gay, J., Shepherd, O., Thyden, M., and Whitman, M. (2010). The health effects of oil contamination: A compilation of research. Worcester Polytechnic Institute. Worcester MA, EUA, 211 pp. |
[9] | Jain, P. K., Gupta, V. K., Gaur, R. K., Lowry, M., Jaroli, D. P., and Chauhan, U. K. (2011) Bioremediation of petroleum oil contaminated soil and water. Research Journal of Environmental Toxicology. 5 (1), 1-26. |
[10] | EPA. United States, Environmental Protection Agency. (2021). Management of Oil and Gas Exploration and Production Waste. Official website use.gov. |
[11] | Neff, J., Lee, K., and DeBlois, E. M. (2011). Produced Water: Overview of Composition, Fates, and Effects. Produced Water, 3–54. doi: 10.1007/978-1-4614-0046-2_1. |
[12] | Islam, B. (2015). Petroleum sludge, its treatment and disposal: A review. Int. J. Chem. Sci. 13 (4), 1584-1602. |
[13] | Infante C., Vásquez, P., and Lippke, M. (1999). Petróleo y Ambiente. Visión Tecnológica (Edición Especial). pp. 99-106. |
[14] | Liendo, F., Serrano, C., Urich, J., Díaz A., Morales, G., and López-Hernández, D. (1991). Tratamiento y disposición de efluentes de perforación en el área de El Furrial, Edo. Monagas. Revista Técnica Intevep. 11, 173-182. |
[15] | López-Hernández, I. D., Hernández, C., Liendo, F., Urich, J., and Vallejo-Torres, O. (2020). Efectos de las aguas residuales de pozos petroleros sobre los suelos de la sabanas cerca de El Furrial, Edo Monagas, Venezuela. Rev. Int. Contam. Ambie., 36 (3), 835-845. doi: https://doi.org/10.20937/RICA.53600. |
[16] | Thamer, J. M., and Esraa R. A. (2017). Turbidity and oil removal from oil field produced water, by coagulation-flocculation technique. The Eighth Jordan International Chemical Engineering Conference (JIChEC 2017) November 7-9. pp. 1-8. |
[17] | López-Hernández and Infante (2016) López-Hernández, D., and Infante C. (2016). N cycle in a Venezuelan sugarcane plantation. How biogeochemical processes contribute to supply N needs. STJ Agri Science. 1 (1), 1003. |
[18] | Van Loop, J. C. (1980). Analytical atomic spectroscopy. Selected methods. Academic Press, Ic. New York, USA. 331 pp. |
[19] | Sampaio Junior, J., Do Amaral, N. M. B., Zonta, E., and Magalhães M. O. L. (2015). Barium and sodium in sunflower plants cultivated in soil treated with wastes of drilling of oil well. Revista Brasileira de Engenharia Agrícola e Ambiental. 19, 1100–1106. DOI: 10.1590/1807-1929/agriambi.v19n11p1100-1106. |
[20] | Skoog, D., West D., Holler F. J., and Crouch S. R. (2014). Fundamentals of Analytical Chemistry. Edition 9, Cengage. Learning US. 1072 pp. |
[21] | Choudhury, H., and Cary, R. (2001). Barium and barium compounds. Concise International Chemical Assessment Document 33. World Health Organization, Geneva, 2001. 57 pp. |
[22] | Weil, R. R., and Brady N. C. (2017). The nature and properties of soil. 15th edition. Pearson Press. Nueva York, EUA, 1104 pp. |
[23] | Lindsay, W. L. (2001). Chemical equilibria in soils. John Wiley and Sons, Inc. 2001. 472 pp. |
[24] | Rowe, D. R., and Abdel-Magid. I. M. (1995). Handbook of Wastewater Reclamation and Reuse. CRC Press, Inc. 550 pp. |
[25] | Franceschi, A., Girou, A., Carro-Diaz, A. M., Maurette, M. T., and Puech-Costes, E. (2002). Optimisation of the coagulation–flocculation process of raw water by optimal design method. Water Research. 36, 3561-3572. |
[26] | Vatanparast, S. (2016). Improved techniques, mixing units can minimize crew exposure to caustic soda on drilling rigs. Drilling Contractor, Drilling it safely, January-February. 2p. |
[27] | Ismail, A. R., Alias, A. H., Sulaiman, W. R. W., and Jaafar M. Z. (2017). Drilling fluid waste management in drilling for oil and gas wells. Chemical Engineering Transactions. 56, 1351-1356. |
[28] | Shrivastava, P., y Kumar, R. (2015). Soil salinity: A serious environmental issue and plant growth promoting bacteria as one of the tools for its alleviation. Saudi J. Biol. Sci. 22 (2), 123-131. DOI: https://doi.org/10.1007/978-3-319-96190-3. |
[29] | Shahid, S. A., Zaman M., and Heng L. (2018) Introduction to Soil Salinity, Sodicity and Diagnostics Techniques. In: Guideline for Salinity Assessment, Mitigation and Adaptation Using Nuclear and Related Techniques. Springer, Cham. 1-42. |
[30] | Beadecker M., Cozzarelli I., and Engahouse R. 1993. Crude oil in a shallow sand and gravel aquifer – III. Biogeochemical reactions and mass balance modeling in anoxic groundwater. Applied geochemistry 8: 569-586. |
APA Style
Danilo López-Hernández, Oswaldo Vallejo-Torres, Fernando Liendo, Juan Urich, Carmen Hernández. (2021). Disposition of Wastewater from Oil Wells in Venezuelan Savannahs and Their Effects on Percolation Waters. Journal of Chemical, Environmental and Biological Engineering, 5(2), 62-68. https://doi.org/10.11648/j.jcebe.20210502.14
ACS Style
Danilo López-Hernández; Oswaldo Vallejo-Torres; Fernando Liendo; Juan Urich; Carmen Hernández. Disposition of Wastewater from Oil Wells in Venezuelan Savannahs and Their Effects on Percolation Waters. J. Chem. Environ. Biol. Eng. 2021, 5(2), 62-68. doi: 10.11648/j.jcebe.20210502.14
AMA Style
Danilo López-Hernández, Oswaldo Vallejo-Torres, Fernando Liendo, Juan Urich, Carmen Hernández. Disposition of Wastewater from Oil Wells in Venezuelan Savannahs and Their Effects on Percolation Waters. J Chem Environ Biol Eng. 2021;5(2):62-68. doi: 10.11648/j.jcebe.20210502.14
@article{10.11648/j.jcebe.20210502.14, author = {Danilo López-Hernández and Oswaldo Vallejo-Torres and Fernando Liendo and Juan Urich and Carmen Hernández}, title = {Disposition of Wastewater from Oil Wells in Venezuelan Savannahs and Their Effects on Percolation Waters}, journal = {Journal of Chemical, Environmental and Biological Engineering}, volume = {5}, number = {2}, pages = {62-68}, doi = {10.11648/j.jcebe.20210502.14}, url = {https://doi.org/10.11648/j.jcebe.20210502.14}, eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.jcebe.20210502.14}, abstract = {In the eastern Venezuelan Llanos, the drilling fluids composed of wastewater (WW), accompanying hydrocarbons and wastes from oil activity are deposited in a system of waterproofed pits. Later, by means of siphons, the hydrocarbon phase of the WW is separated. WW are typically very salty and contain suspended and dissolved solids, residual hydrocarbons, and chemicals used in hydrocarbon extraction. So they are transported to a pit and treated with a flocculating agent and lime. Once carried out, the flocculation-coagulation operation and pH correction, WW are released to the environment. The savannas where the treated water are irrigated, in addition to the oil operation, present an intense agricultural and livestock activity, and rest on aquifers that are partially replenished with the percolation waters near the treatment pits. Therefore, this research will aim to analyze: i) the levels of soluble salts and heavy metals in the percolation waters collected in lysimeters located in savanna soils adjacent to oil wells after irrigation with WW treated with flocculating agents, and ii) the estimation of time which these salts take to be dislodged from the soil. The waters from the lysimeters did not report high levels of soluble aluminum or heavy metals since their soluble forms were precipitated by liming. Likewise, the coagulation-flocculation process removed the high levels of barium from the untreated WW. The contributions of sodium and calcium from the WW have a liming effect on the acidity of these soils. The sodium levels contributed by the WW could represent an environmental risk, fortunately, the good internal drainage of these sandy Ultisols allows their removal. Studies with lysimeters showed that the percolation waters of areas irrigated with flocculated water have a similar sodium content to that of control lysimeters six months after treatment.}, year = {2021} }
TY - JOUR T1 - Disposition of Wastewater from Oil Wells in Venezuelan Savannahs and Their Effects on Percolation Waters AU - Danilo López-Hernández AU - Oswaldo Vallejo-Torres AU - Fernando Liendo AU - Juan Urich AU - Carmen Hernández Y1 - 2021/11/05 PY - 2021 N1 - https://doi.org/10.11648/j.jcebe.20210502.14 DO - 10.11648/j.jcebe.20210502.14 T2 - Journal of Chemical, Environmental and Biological Engineering JF - Journal of Chemical, Environmental and Biological Engineering JO - Journal of Chemical, Environmental and Biological Engineering SP - 62 EP - 68 PB - Science Publishing Group SN - 2640-267X UR - https://doi.org/10.11648/j.jcebe.20210502.14 AB - In the eastern Venezuelan Llanos, the drilling fluids composed of wastewater (WW), accompanying hydrocarbons and wastes from oil activity are deposited in a system of waterproofed pits. Later, by means of siphons, the hydrocarbon phase of the WW is separated. WW are typically very salty and contain suspended and dissolved solids, residual hydrocarbons, and chemicals used in hydrocarbon extraction. So they are transported to a pit and treated with a flocculating agent and lime. Once carried out, the flocculation-coagulation operation and pH correction, WW are released to the environment. The savannas where the treated water are irrigated, in addition to the oil operation, present an intense agricultural and livestock activity, and rest on aquifers that are partially replenished with the percolation waters near the treatment pits. Therefore, this research will aim to analyze: i) the levels of soluble salts and heavy metals in the percolation waters collected in lysimeters located in savanna soils adjacent to oil wells after irrigation with WW treated with flocculating agents, and ii) the estimation of time which these salts take to be dislodged from the soil. The waters from the lysimeters did not report high levels of soluble aluminum or heavy metals since their soluble forms were precipitated by liming. Likewise, the coagulation-flocculation process removed the high levels of barium from the untreated WW. The contributions of sodium and calcium from the WW have a liming effect on the acidity of these soils. The sodium levels contributed by the WW could represent an environmental risk, fortunately, the good internal drainage of these sandy Ultisols allows their removal. Studies with lysimeters showed that the percolation waters of areas irrigated with flocculated water have a similar sodium content to that of control lysimeters six months after treatment. VL - 5 IS - 2 ER -