Adsorption of herbicide, glyphosate, 2-[(phosphonomethyl) amino] acetic acid onto locally derived adsorbent: an ftir – gcms approach in qualitative analysis

Adsorption of herbicide, glyphosate, 2-[(phosphonomethyl) amino] acetic acid onto locally derived adsorbent: an ftir – gcms approach in qualitative analysis

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Article_Title: Adsorption of herbicide, glyphosate, 2-[(phosphonomethyl) amino] acetic acid onto locally derived adsorbent: an ftir – gcms approach in qualitative analysis
Authors: Itodo A.U. *, Adetunji I.I., Itodo H.U., Gafar M.K., Usman A.
Affiliation: Department of Chemical Sciences, Federal University, Wukari, Nigeria
Department of Applied Chemistry, Kebbi State University of Science and Technology, Aliero, Nigeria
Department of Chemistry, Benue state University Makurdi, Nigeria.
Department of Chemistry, Federal University Dutsinma, Katsina State, Nigeria.
Basic Science Unit, Nasarawa State University Keffi, Shabu-Lafia Campus, Keffi, Nigeria
Abstract: The adsorption of unsuspected pollutant, an orgarno-phosphorus herbicide with the general name; glyphosate, trade name; Roundupand chemically called 2-[(phosphonomethyl) amino] acetic acid or N-(phosphonomethyl) glycine was qualitatively investigated. A batch adsorption mode was utilized as reactor in interacting herbicide solution with derived activated carbon. Results obtained from FTIR and GCMS run revealed the phenomenon likened to the adsorption of certain functional groups from the herbicide viz; NH-Amine (peak range of 3300-3500 cm-1), polyoxyethyleneaminein glyphosate herbicides,CO Carbonyl groups (3412.19cm-1 peak region), OH-groups (3200-3600 cm-1peak region) and phosphonic moiety. On comparing the original herbicide spectral with those interacted with activated carbon, the functional groups common to both had different peaks information (denoting different peak heights, intensities and types of vibrations). This is an indication that there could be possibilities of either partial adsorption as observed from band shift, band distortion and not necessarily a band disappearance as applicable to complete or total adsorption. The role played by solvent action was also discussed.
Keywords: Glyphosate, Herbicide, Adsorption, Activated Carbon, FTIR, GCMS
References: Agdi K, Bouaid A, Martin E, Fernandez H, Azmani A Camara, Removal of atrazine from environmental water by diatomaceous earth remediation method. J. Environ. Monitor, 2, 420- 423, 2000. Ahmedna M, Marshal W, and Rao M, Production of Granular activated carbon from selected Agric bye products. Bioresources Technology; 71(2): 113-123, 2000. Albers BG, Hansen P, Jacobsen O, The influence of organic matter on sorption and fate of glyphosate in soil comparing different soils and humic substances, Environmental pollution, 157 (10), 2865–2870, 2009. Aziza A, Odiakosa G, Nwajei, V. Orodu V, Modification and characterization of activated carbon derived from Bumper sawdust and disk sawdust to remove lead (II) and cadmium (II) effluent water. CSN Conference proceeding. Chemical Society of Nigeria, Deltachem, pp, 235-243, 2008. Daruich J, Zirulnik F, Gimenez MS, Effect of the herbicide glyphosate on enzymatic activity in pregnant rats and their fetuses, Environmental Research 85 (3), 226–31, 2001. Hanson KG, Fernandez MR, In-vitro growth of fusarium head blight as affected by glyphosate-based herbicides. Canadian Journal of Plant Pathology, 25,120, 2003. Feng, JC, Thompson DG, Reynolds PE, Fate of Glyphosate in a Canadian Forest Watershed. 1. Aquatic Residues and Off Target Deposit Assessment. J. Agric. Food Chem. 38, 1110-111. 1990. Gardner S, Grue C, Effects of Rodeo and Garlon 3A on Nontarget Wetland Species In Central Washington. Environ Toxicol Chem, Bol 15, ( 4), 441-451, 1996. Giesy JP, Dobson S, Solomon KR, Ecotoxicological Risk Assessment for Roundup Herbicide. Rev Env. ContamToxicol, 167,35-120, 2000. Graves L, Roundup Birth Defects: Regulators Knew World’s Best-Selling Herbicide Causes Problems, New Report Finds, Huffington Post, 9, 2011. Hanson KG, Fernandez MR, In-vitro growth of fusarium head blight as affected by glyphosate-based herbicides. Canadian Journal of Plant Pathology,25,120, 2003. Igwe JC, Abia AA, Maize cob and husk as adsorbent for removal Cd, Pb and Zn ions from waste water. The physical science, 2, 83-94, 2003. Itodo AU, Abdulrahman FW, Hassan LG., Atiku FA, Itodo HU, GCMS Prediction of Organochlorine Herbicide Sorption Rate: A Batch Kinetic Studies, Trends in Applied Sciences Research, 6(8), 451-462, 2011.Itodo AU, Abdulrahman FW, Hassan LG, Maigandi SA, Itodo HU, Gas Chromatographic Prediction of Equilibrium Phase Atrazine after Sorption onto Derived Activated Carbon, International Journal of Poultry Science, 8, 1174-1182, 2009. LaGrega M, Buckingham P, Evans J, Environmental Resources Management Group, Hazardous Waste Management, McGraw-Hill Inc.,New York, NY ,1994. Mann RM, Bidwell JR. The toxicity of glyphosate and several glyphosate formulations to four species of Southwestern Australian Frogs. Arch Environ contam. Toxical. 36, 193-199, 1999: In Mann, RM, Toxicological impact of agricultural surfactants on Australian amphibians. Curtin University of Technology, Sydney, Australia. Available at http://adt.curtin.edu.au/theses/available/adt-WCU20031202.161329/ ,2000. Martinez TT, Brown K, Oral and pulmonary toxicity of the surfactant used in Roundup herbicide. Proc. West. Pharmacol. Soc, 34,43-46, 1991. Richard S, Moslemi S, Sipahutar H, Benachour N, and Seralini GE, Differential effects of glyphosate and Roundup on human placental cells and aromatase. Environ. Health Perspect, 113, 716–720, 2005. Rueppel ML, Brightwell BB, Schaefer J, and Marvel JT, Metabolism and degradation of glyphosate in soil and water. J. Agric. Food Chem. 25,517-528, 1977. Thompson J, Chronic effects of sub-lethal levels of dalapon, gluphosate and 2,4-D amine on the lymnaeid snails pseudo succineacolumella and Fossariacubensis, M.S thesis, southern University Library, Baton Rouge, L.A, 1989. Torstensson L, Behavior of glyphosate in soils and its degradation, The Herbicide Glyphosate, Chap, Swedish University of Agricultural Sciences, Upsala, Sweden, 9, 137-150, 1985. U.S. EPA, Pesticide Fact Handbook, Noyes Data Corporation, Park Ridge, New Jersey, 2, 301-312, . 1990. Walsh L P, McCormick C, Martin C, Stocco DM, Roundup inhibits steroidogenesis by disrupting steroidogenic acute regulatory (StAR) protein expression, Environmental health perspectives Environmental Health Perspectives, 108, 8, 769–776, 2000. Williams GM, Kroes R, Munro IC, Safety evaluation and risk assessment of the herbicide Roundup and its active ingredient, glyphosate for humans, Regulatory Toxicol and Pharmacol. 31,117–165, 2000. Who, Glyphosate. Environmental Health Criteria No.
Read_full_article: http://studiauniversitatis.ro/v15/pdf/23-2013/23-4-2013/SU23-4-2013-Tit.pdf
Correspondence: Dr. Adams Udoji Itodo, Federal University, Wukari, Department of Chemical Sciences, Nigeria. TEL: +234(0)8039503463 Email: itodoson2002@gmail.com

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Article Title: Adsorption of herbicide, glyphosate, 2-[(phosphonomethyl) amino] acetic acid onto locally derived adsorbent: an ftir – gcms approach in qualitative analysis
Authors: Itodo A.U. *, Adetunji I.I., Itodo H.U., Gafar M.K., Usman A.
Affiliation: Department of Chemical Sciences, Federal University, Wukari, Nigeria
Department of Applied Chemistry, Kebbi State University of Science and Technology, Aliero, Nigeria
Department of Chemistry, Benue state University Makurdi, Nigeria.
Department of Chemistry, Federal University Dutsinma, Katsina State, Nigeria.
Basic Science Unit, Nasarawa State University Keffi, Shabu-Lafia Campus, Keffi, Nigeria
Abstract: The adsorption of unsuspected pollutant, an orgarno-phosphorus herbicide with the general name; glyphosate, trade name; Roundupand chemically called 2-[(phosphonomethyl) amino] acetic acid or N-(phosphonomethyl) glycine was qualitatively investigated. A batch adsorption mode was utilized as reactor in interacting herbicide solution with derived activated carbon. Results obtained from FTIR and GCMS run revealed the phenomenon likened to the adsorption of certain functional groups from the herbicide viz; NH-Amine (peak range of 3300-3500 cm-1), polyoxyethyleneaminein glyphosate herbicides,CO Carbonyl groups (3412.19cm-1 peak region), OH-groups (3200-3600 cm-1peak region) and phosphonic moiety. On comparing the original herbicide spectral with those interacted with activated carbon, the functional groups common to both had different peaks information (denoting different peak heights, intensities and types of vibrations). This is an indication that there could be possibilities of either partial adsorption as observed from band shift, band distortion and not necessarily a band disappearance as applicable to complete or total adsorption. The role played by solvent action was also discussed.
Keywords: Glyphosate, Herbicide, Adsorption, Activated Carbon, FTIR, GCMS
References: Agdi K, Bouaid A, Martin E, Fernandez H, Azmani A Camara, Removal of atrazine from environmental water by diatomaceous earth remediation method. J. Environ. Monitor, 2, 420- 423, 2000. Ahmedna M, Marshal W, and Rao M, Production of Granular activated carbon from selected Agric bye products. Bioresources Technology; 71(2): 113-123, 2000. Albers BG, Hansen P, Jacobsen O, The influence of organic matter on sorption and fate of glyphosate in soil comparing different soils and humic substances, Environmental pollution, 157 (10), 2865–2870, 2009. Aziza A, Odiakosa G, Nwajei, V. Orodu V, Modification and characterization of activated carbon derived from Bumper sawdust and disk sawdust to remove lead (II) and cadmium (II) effluent water. CSN Conference proceeding. Chemical Society of Nigeria, Deltachem, pp, 235-243, 2008. Daruich J, Zirulnik F, Gimenez MS, Effect of the herbicide glyphosate on enzymatic activity in pregnant rats and their fetuses, Environmental Research 85 (3), 226–31, 2001. Hanson KG, Fernandez MR, In-vitro growth of fusarium head blight as affected by glyphosate-based herbicides. Canadian Journal of Plant Pathology, 25,120, 2003. Feng, JC, Thompson DG, Reynolds PE, Fate of Glyphosate in a Canadian Forest Watershed. 1. Aquatic Residues and Off Target Deposit Assessment. J. Agric. Food Chem. 38, 1110-111. 1990. Gardner S, Grue C, Effects of Rodeo and Garlon 3A on Nontarget Wetland Species In Central Washington. Environ Toxicol Chem, Bol 15, ( 4), 441-451, 1996. Giesy JP, Dobson S, Solomon KR, Ecotoxicological Risk Assessment for Roundup Herbicide. Rev Env. ContamToxicol, 167,35-120, 2000. Graves L, Roundup Birth Defects: Regulators Knew World’s Best-Selling Herbicide Causes Problems, New Report Finds, Huffington Post, 9, 2011. Hanson KG, Fernandez MR, In-vitro growth of fusarium head blight as affected by glyphosate-based herbicides. Canadian Journal of Plant Pathology,25,120, 2003. Igwe JC, Abia AA, Maize cob and husk as adsorbent for removal Cd, Pb and Zn ions from waste water. The physical science, 2, 83-94, 2003. Itodo AU, Abdulrahman FW, Hassan LG., Atiku FA, Itodo HU, GCMS Prediction of Organochlorine Herbicide Sorption Rate: A Batch Kinetic Studies, Trends in Applied Sciences Research, 6(8), 451-462, 2011.Itodo AU, Abdulrahman FW, Hassan LG, Maigandi SA, Itodo HU, Gas Chromatographic Prediction of Equilibrium Phase Atrazine after Sorption onto Derived Activated Carbon, International Journal of Poultry Science, 8, 1174-1182, 2009. LaGrega M, Buckingham P, Evans J, Environmental Resources Management Group, Hazardous Waste Management, McGraw-Hill Inc.,New York, NY ,1994. Mann RM, Bidwell JR. The toxicity of glyphosate and several glyphosate formulations to four species of Southwestern Australian Frogs. Arch Environ contam. Toxical. 36, 193-199, 1999: In Mann, RM, Toxicological impact of agricultural surfactants on Australian amphibians. Curtin University of Technology, Sydney, Australia. Available at http://adt.curtin.edu.au/theses/available/adt-WCU20031202.161329/ ,2000. Martinez TT, Brown K, Oral and pulmonary toxicity of the surfactant used in Roundup herbicide. Proc. West. Pharmacol. Soc, 34,43-46, 1991. Richard S, Moslemi S, Sipahutar H, Benachour N, and Seralini GE, Differential effects of glyphosate and Roundup on human placental cells and aromatase. Environ. Health Perspect, 113, 716–720, 2005. Rueppel ML, Brightwell BB, Schaefer J, and Marvel JT, Metabolism and degradation of glyphosate in soil and water. J. Agric. Food Chem. 25,517-528, 1977. Thompson J, Chronic effects of sub-lethal levels of dalapon, gluphosate and 2,4-D amine on the lymnaeid snails pseudo succineacolumella and Fossariacubensis, M.S thesis, southern University Library, Baton Rouge, L.A, 1989. Torstensson L, Behavior of glyphosate in soils and its degradation, The Herbicide Glyphosate, Chap, Swedish University of Agricultural Sciences, Upsala, Sweden, 9, 137-150, 1985. U.S. EPA, Pesticide Fact Handbook, Noyes Data Corporation, Park Ridge, New Jersey, 2, 301-312, . 1990. Walsh L P, McCormick C, Martin C, Stocco DM, Roundup inhibits steroidogenesis by disrupting steroidogenic acute regulatory (StAR) protein expression, Environmental health perspectives Environmental Health Perspectives, 108, 8, 769–776, 2000. Williams GM, Kroes R, Munro IC, Safety evaluation and risk assessment of the herbicide Roundup and its active ingredient, glyphosate for humans, Regulatory Toxicol and Pharmacol. 31,117–165, 2000. Who, Glyphosate. Environmental Health Criteria No.
*Correspondence: Dr. Adams Udoji Itodo, Federal University, Wukari, Department of Chemical Sciences, Nigeria. TEL: +234(0)8039503463 Email: itodoson2002@gmail.com