Residues of organochlorine and organophosphorus pesticides in sugarcane crop soils and river water
The presence of residual organochlorine and organophosphorus pesticides was evaluated at different periods of sugarcane cultivation in agricultural soil and water samples from the town of Tlaltizapan, which is located in the state of Morelos in Mexico, to determine the presence and persistence of th...
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| Published in: | Journal of environmental science and health. Part B, Pesticides, food contaminants, and agricultural wastes Vol. 47; no. 9; pp. 833 - 841 |
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| Main Authors: | , , , |
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| Language: | English |
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01-10-2012
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| Abstract | The presence of residual organochlorine and organophosphorus pesticides was evaluated at different periods of sugarcane cultivation in agricultural soil and water samples from the town of Tlaltizapan, which is located in the state of Morelos in Mexico, to determine the presence and persistence of these compounds and their possible effects on the region. The compounds p,p′-DDE, p,p′-DDD (metabolites of p,p′-DDT), γ-HCH and heptachlor were found in more of 95% of the sampling zones in the three monitoring periods performed along 2 years. The highest concentration detected (129.6 μg/kg dᵣy ₛₒᵢₗ) was for α-HCH, but its frequency of detection was ∼5%. The low detection frequency of α-HCH and the high concentration values of γ-HCH indicate the repeated use of technical-grade HCH and Lindane (γ-HCH) in the region. Among the organophosphorus pesticides, ethyl parathion was the compound with the highest soil concentration, at ∼2000 μg/kgdᵣy ₛₒᵢₗ, during the initial monitoring. However, this compound was detected in the second monitoring with a concentration of ∼4 μg/kgdᵣy ₛₒᵢₗ, but it was not detected in the third, indicating that is was not accumulated in the environment. The heptachlor was the compound most commonly found in all water samples, within a range of 0.45–1.25 ng/L. The presence of this organochlorine compound in the water samples indicated a possible migration from the soil to water bodies due to soil erosion. The presence of organophosphorus compounds was not detected in the water samples, which could be attributed to the moderate persistence of these compounds and their consequent degradation before arriving at the water bodies. |
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| AbstractList | The presence of residual organochlorine and organophosphorus pesticides was evaluated at different periods of sugarcane cultivation in agricultural soil and water samples from the town of Tlaltizapan, which is located in the state of Morelos in Mexico, to determine the presence and persistence of these compounds and their possible effects on the region. The compounds p,p′-DDE, p,p′-DDD (metabolites of p,p′-DDT), γ-HCH and heptachlor were found in more of 95% of the sampling zones in the three monitoring periods performed along 2 years. The highest concentration detected (129.6 μg/kg
dry soil
) was for α-HCH, but its frequency of detection was ∼5%. The low detection frequency of α-HCH and the high concentration values of γ-HCH indicate the repeated use of technical-grade HCH and Lindane (γ-HCH) in the region. Among the organophosphorus pesticides, ethyl parathion was the compound with the highest soil concentration, at ∼2000 μg/kg
dry soil
, during the initial monitoring. However, this compound was detected in the second monitoring with a concentration of ∼4 μg/kg
dry soil
, but it was not detected in the third, indicating that is was not accumulated in the environment. The heptachlor was the compound most commonly found in all water samples, within a range of 0.45-1.25 ng/L. The presence of this organochlorine compound in the water samples indicated a possible migration from the soil to water bodies due to soil erosion. The presence of organophosphorus compounds was not detected in the water samples, which could be attributed to the moderate persistence of these compounds and their consequent degradation before arriving at the water bodies. The presence of residual organochlorine and organophosphorus pesticides was evaluated at different periods of sugarcane cultivation in agricultural soil and water samples from the town of Tlaltizapan, which is located in the state of Morelos in Mexico, to determine the presence and persistence of these compounds and their possible effects on the region. The compounds p,p′-DDE, p,p′-DDD (metabolites of p,p′-DDT), γ-HCH and heptachlor were found in more of 95% of the sampling zones in the three monitoring periods performed along 2 years. The highest concentration detected (129.6 μg/kg dᵣy ₛₒᵢₗ) was for α-HCH, but its frequency of detection was ∼5%. The low detection frequency of α-HCH and the high concentration values of γ-HCH indicate the repeated use of technical-grade HCH and Lindane (γ-HCH) in the region. Among the organophosphorus pesticides, ethyl parathion was the compound with the highest soil concentration, at ∼2000 μg/kgdᵣy ₛₒᵢₗ, during the initial monitoring. However, this compound was detected in the second monitoring with a concentration of ∼4 μg/kgdᵣy ₛₒᵢₗ, but it was not detected in the third, indicating that is was not accumulated in the environment. The heptachlor was the compound most commonly found in all water samples, within a range of 0.45–1.25 ng/L. The presence of this organochlorine compound in the water samples indicated a possible migration from the soil to water bodies due to soil erosion. The presence of organophosphorus compounds was not detected in the water samples, which could be attributed to the moderate persistence of these compounds and their consequent degradation before arriving at the water bodies. The presence of residual organochlorine and organophosphorus pesticides was evaluated at different periods of sugarcane cultivation in agricultural soil and water samples from the town of Tlaltizapan, which is located in the state of Morelos in Mexico, to determine the presence and persistence of these compounds and their possible effects on the region. The compounds p,p'-DDE, p,p'-DDD (metabolites of p,p'-DDT), gamma -HCH and heptachlor were found in more of 95% of the sampling zones in the three monitoring periods performed along 2 years. The highest concentration detected (129.6 mu g/kg sub(dry soil)) was for alpha -HCH, but its frequency of detection was similar to 5%. The low detection frequency of alpha -HCH and the high concentration values of gamma -HCH indicate the repeated use of technical-grade HCH and Lindane ( gamma -HCH) in the region. Among the organophosphorus pesticides, ethyl parathion was the compound with the highest soil concentration, at similar to 2000 mu g/kg sub(dry soil), during the initial monitoring. However, this compound was detected in the second monitoring with a concentration of similar to 4 mu g/kg sub(dry soil), but it was not detected in the third, indicating that is was not accumulated in the environment. The heptachlor was the compound most commonly found in all water samples, within a range of 0.45-1.25 ng/L. The presence of this organochlorine compound in the water samples indicated a possible migration from the soil to water bodies due to soil erosion. The presence of organophosphorus compounds was not detected in the water samples, which could be attributed to the moderate persistence of these compounds and their consequent degradation before arriving at the water bodies. The presence of residual organochlorine and organophosphorus pesticides was evaluated at different periods of sugarcane cultivation in agricultural soil and water samples from the town of Tlaltizapan, which is located in the state of Morelos in Mexico, to determine the presence and persistence of these compounds and their possible effects on the region. The compounds p,p'-DDE, p,p'-DDD (metabolites of p,p'-DDT), ...-HCH and heptachlor were found in more of 95% of the sampling zones in the three monitoring periods performed along 2 years. The highest concentration detected (129.6 ...g/kg...) was for α-HCH, but its frequency of detection was ~5%. The low detection frequency of α-HCH and the high concentration values of ...-HCH indicate the repeated use of technical-grade HCH and Lindane (...-HCH) in the region. Among the organophosphorus pesticides, ethyl parathion was the compound with the highest soil concentration, at ~2000 ...g/kg..., during the initial monitoring. However, this compound was detected in the second monitoring with a concentration of ~4 ...g/kg..., but it was not detected in the third, indicating that is was not accumulated in the environment. The heptachlor was the compound most commonly found in all water samples, within a range of 0.45-1.25 ng/L. The presence of this organochlorine compound in the water samples indicated a possible migration from the soil to water bodies due to soil erosion. The presence of organophosphorus compounds was not detected in the water samples, which could be attributed to the moderate persistence of these compounds and their consequent degradation before arriving at the water bodies. (ProQuest: ... denotes formulae/symbols omitted.) |
| Author | Velasco, Antonio Ortíz, Irmene Rodríguez, Jorge Castillo, Rocío |
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| Cites_doi | 10.1021/es030038m 10.1021/jf025978p 10.1021/es040624v 10.1016/j.chemosphere.2010.08.049 10.1021/es803294w 10.1016/j.scitotenv.2006.09.023 10.1039/b202598a 10.1021/jf040250p 10.1351/pac199769061349 10.1021/es070870h 10.1080/00288233.1995.9513126 10.1021/es990647n 10.1021/es9708530 10.1016/S0048-9697(00)00877-9 10.1016/S0045-6535(03)00477-6 10.1021/es051677v 10.1021/es0262535 |
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| Keywords | Saccharum Monocotyledones hexachlorocyclohexane Insecticide Pesticides Agricultural soil HCH Sugar plant sugarcane Gramineae DDT Organochlorine compounds Residue Angiospermae Environment Spermatophyta Sugar cane Organophosphorus compounds River water |
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| References | CIT0010 Agency for Toxic Substances and Disease Registry (ATSDR) (CIT0003) 2002 Instituto Nacional de Ecología (INE) (CIT0005) 2004 US Environmental Protection Agency (US EPA) (CIT0029) 1999 US Environmental Protection Agency (US EPA) (CIT0014) 2007 Diario oficial de la Federación (DOF) (CIT0002) 1991 Escobar J. L. (CIT0006) 2005 Zitko V. (CIT0001) 2003 US Environmental Protection Agency (US EPA) (CIT0013) 2007 CIT0016 CIT0015 CIT0018 CIT0017 CIT0019 CIT0021 Rodríguez S. (CIT0007) 2006; 6 CIT0023 US Environmental Protection Agency (US EPA) (CIT0011) 2007 CIT0022 Umrit G. (CIT0030) 1999; 73 Díaz-Barriga F. (CIT0020) 2003 CIT0025 CIT0024 CIT0027 CIT0004 CIT0026 CIT0028 CIT0009 US Environmental Protection Agency (US EPA) (CIT0012) 1996 CIT0008 |
| References_xml | – start-page: 371 volume-title: The Handbook of Environmental Chemistry. Vol. 3 Part O: Persistent organic pollutant year: 2003 ident: CIT0020 contributor: fullname: Díaz-Barriga F. – volume-title: Caracterización de suelos contaminados con plaguicidas organoclorados, para su biorremediación year: 2005 ident: CIT0006 contributor: fullname: Escobar J. L. – ident: CIT0019 doi: 10.1021/es030038m – volume-title: Organochlorine Pesticides by Gas Chromatography, Method 8081B year: 2007 ident: CIT0013 contributor: fullname: US Environmental Protection Agency (US EPA) – ident: CIT0028 doi: 10.1021/jf025978p – ident: CIT0018 doi: 10.1021/es040624v – volume-title: El Lindano en México year: 2004 ident: CIT0005 contributor: fullname: Instituto Nacional de Ecología (INE) – ident: CIT0021 doi: 10.1016/j.chemosphere.2010.08.049 – volume-title: Semivolatile Organic Compounds, Method 8270D year: 2007 ident: CIT0014 contributor: fullname: US Environmental Protection Agency (US EPA) – volume-title: Separatory Funnel Liquid-Liquid Extraction 3510C year: 1996 ident: CIT0012 contributor: fullname: US Environmental Protection Agency (US EPA) – ident: CIT0025 doi: 10.1021/es803294w – ident: CIT0016 doi: 10.1016/j.scitotenv.2006.09.023 – ident: CIT0017 doi: 10.1039/b202598a – ident: CIT0008 doi: 10.1021/jf040250p – volume-title: Relación de plaguicidas prohibidos para su importación, fabricación, formulación, comercialización y uso en México year: 1991 ident: CIT0002 contributor: fullname: Diario oficial de la Federación (DOF) – volume-title: Toxicological profile for DDT, DDD and DDE year: 2002 ident: CIT0003 contributor: fullname: Agency for Toxic Substances and Disease Registry (ATSDR) – ident: CIT0027 doi: 10.1351/pac199769061349 – volume-title: Office of Environmental Health Hazard Assessment year: 1999 ident: CIT0029 contributor: fullname: US Environmental Protection Agency (US EPA) – volume-title: Ultrasonic Extraction, Method 3550C year: 2007 ident: CIT0011 contributor: fullname: US Environmental Protection Agency (US EPA) – volume: 6 start-page: 77 issue: 1 year: 2006 ident: CIT0007 publication-title: AGROFAZ contributor: fullname: Rodríguez S. – ident: CIT0009 doi: 10.1021/es070870h – ident: CIT0015 doi: 10.1080/00288233.1995.9513126 – ident: CIT0004 doi: 10.1021/es990647n – ident: CIT0022 doi: 10.1021/es9708530 – ident: CIT0026 doi: 10.1016/S0048-9697(00)00877-9 – ident: CIT0023 doi: 10.1016/S0045-6535(03)00477-6 – ident: CIT0010 doi: 10.1021/es051677v – volume: 73 start-page: 24 year: 1999 ident: CIT0030 publication-title: Proceedings of the Congress of the South African Sugar Technologists Association contributor: fullname: Umrit G. – start-page: 48 volume-title: The Handbook of Environmental Chemistry; Vol. 3 Part O: Persistent organic pollutants year: 2003 ident: CIT0001 contributor: fullname: Zitko V. – ident: CIT0024 doi: 10.1021/es0262535 |
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| SubjectTerms | agricultural soil agricultural soils Agronomy. Soil science and plant productions Animal, plant and microbial ecology Applied ecology Biodegradation Biological and medical sciences Chemical compounds Control DDT Environmental monitoring Environmental testing Freshwater Fundamental and applied biological sciences. Psychology HCH (pesticide) heptachlor hexachlorocyclohexane lindane metabolites monitoring parathion ethyl Pesticides Phytopathology. Animal pests. Plant and forest protection Protozoa. Invertebrates river water Soil erosion soil water sugarcane surface water |
| Title | Residues of organochlorine and organophosphorus pesticides in sugarcane crop soils and river water |
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