Critical consideration of the multiplicity of experimental and organismic determinants of pyrethroid neurotoxicity: A proof of concept
Pyrethroids (PYR) are pesticides with high insecticidal activity that may disrupt neuronal excitability in target and nontarget species. The accumulated evidence consistently showed that this neurophysiologic action is followed by alterations in motor, sensorimotor, neuromuscular, and thermoregulato...
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2013
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| LEADER | 57566caa a22036737a 4500 | ||
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| 001 | PAPER-11077 | ||
| 003 | AR-BaUEN | ||
| 005 | 20230518204111.0 | ||
| 008 | 190411s2013 xx ||||fo|||| 00| 0 eng|d | ||
| 024 | 7 | |2 scopus |a 2-s2.0-84892985872 | |
| 024 | 7 | |2 cas |a allethrin, 584-79-2; cyfluthrin, 68359-37-5; phenothrin, 26002-80-2; resmethrin, 10453-86-8; tetramethrin, 7696-12-0; tralomethrin, 66841-25-6; Pyrethrins; Pyrethrins | |
| 040 | |a Scopus |b spa |c AR-BaUEN |d AR-BaUEN | ||
| 030 | |a JTECF | ||
| 100 | 1 | |a Wolansky, M.J. | |
| 245 | 1 | 0 | |a Critical consideration of the multiplicity of experimental and organismic determinants of pyrethroid neurotoxicity: A proof of concept |
| 260 | |b Taylor and Francis Inc. |c 2013 | ||
| 270 | 1 | 0 | |m Wolansky, M.J.; Laboratorio de Toxicología de Mezclas Químicas, Departamento Química Biológica, Universidad de Buenos Aires, (UBA), Piso 4, Pabellón 2, Ciudad Autónoma de Buenos Aires (1428EGA), Argentina; email: mjwolansky@qb.fcen.uba.ar |
| 506 | |2 openaire |e Política editorial | ||
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| 504 | |a Williamson, E.G., Long, S.F., Kallman, M.J., Wilson, M.C., A comparative analysis of the acute toxicity of technical-grade pyrethroid insecticides and their commercial formulations (1989) Ecotoxicology and Environmental Safety, 18 (1), pp. 27-34 | ||
| 504 | |a Wolansky, M.J., Gennings, C., Crofton, K.M., Relative potencies for acute effects of pyrethroids on motor function in rats (2006) Toxicological Sciences, 89 (1), pp. 271-277. , DOI 10.1093/toxsci/kfj020 | ||
| 504 | |a Wolansky, M.J., Gennings, C., Devito, M.J., Crofton, K.M., Evidence for dose additive effects of pyrethroids on motor activity in rats (2009) Environ. Health Perspect, 117, pp. 1563-1570 | ||
| 504 | |a Wolansky, M.J., McDaniel, K.L., Moser, V.C., Crofton, K.M., Influence of dosing volume on the neurotoxicity of bifenthrin (2007) Neurotoxicology and Teratology, 29 (3), pp. 377-384. , DOI 10.1016/j.ntt.2007.01.007, PII S0892036207000104 | ||
| 504 | |a Wolansky, M.J., Mack, C.M., Becker, P.B., Gordon, C.J., Crofton, K.M., Effects of acute pyrethroid exposure on thermoregulation in rats (2007) Toxicologist, 91, pp. P423 | ||
| 504 | |a Wolansky, M.J., Harrill, J.A., Neurobehavioral toxicology of pyrethroid insecticides in adult animals: A critical review (2008) Neurotoxicol. Teratol, 30, pp. 55-78. , J. A | ||
| 504 | |a Wood, A., (2013) Alan Wood's Compendium of Pesticide Common Names, , http://www.alanwood.net/pesticides/class_pesticides.html, Classified lists of pesticides | ||
| 504 | |a Woudneh, M.B., Oros, D.R., Quantitative determination of pyrethroids, pyrethrins, and piperonyl butoxide in surface water by high-resolution gas chromatography/high-resolution mass spectrometry (2006) Journal of Agricultural and Food Chemistry, 54 (19), pp. 6957-6962. , DOI 10.1021/jf0609431 | ||
| 504 | |a Wu, C., Feng, C., Qi, X., Wang, G., Zheng, M., Chang, X., Zhou, Z., Urinary metabolite levels of pyrethroid insecticides in infants living in an agricultural area of the Province of Jiangsu in China (2013) Chemosphere, 90, pp. 2705-2713 | ||
| 504 | |a Yang, H.-Z., Nishimura, M., Nishimura, K., Kuroda, S., Fujita, T., Quantitative structure-activity studies of pyrethroids. 12. Physicochemical substituent effects of meta-phenoxybenzyl α,α- disubstituted acetates on insecticidal activity (1987) Pesticide Biochemistry and Physiology, 29 (3), pp. 217-232 | ||
| 504 | |a Yang, P.-Y., Lin, J.-L., Hall, A.H., Tsao, T.C.Y., Chern, M.-S., Acute ingestion poisoning with insecticide formulations containing the pyrethroid permethrin, xylene, and surfactant: A review of 48 cases (2002) Journal of Toxicology - Clinical Toxicology, 40 (2), pp. 107-113. , DOI 10.1081/CLT-120004397 | ||
| 504 | |a Zucker, I., Light-dark rhythms in rat eating and drinking behavior (1971) Physiol. Behav, 6, pp. 115-126 | ||
| 520 | 3 | |a Pyrethroids (PYR) are pesticides with high insecticidal activity that may disrupt neuronal excitability in target and nontarget species. The accumulated evidence consistently showed that this neurophysiologic action is followed by alterations in motor, sensorimotor, neuromuscular, and thermoregulatory responses. Nevertheless, there are some equivocal results regarding the potency of PYR in lab animals. The estimation of potency is an important step in pesticide chemical risk assessment. In order to identify the variables influencing neurobehavioral findings across PYR studies, evidence on experimental and organismic determinants of acute PYR-induced neurotoxicity was reviewed in rodents. A comprehensive analysis of these studies was conducted focusing on test material and dosing conditions, testing conditions, animal models, and other determinants such as testing room temperature. Variations in the severity of the neurotoxicity, under lab-controlled conditions, was explained based upon factors including influence of animal species and age, test material features such as chemical structure and stereochemistry, and dosing conditions such as vehicle, route of exposure, and dose volume. If not controlled, the interplay of these factors may lead to large variance in potency estimation. This review examined the scope of acute toxicological data required to determine the safety of pesticide products, and factors and covariates that need to be controlled in order to ensure that predictivity and precaution are balanced in a risk assessment process within a reasonable time-frame, using acute PYR-induced neurotoxicity in rodents as an exemplar. Copyright © 2013 Taylor and Francis Group, LLC. |l eng | |
| 536 | |a Detalles de la financiación: U.S. Environmental Protection Agency | ||
| 536 | |a Detalles de la financiación: Universidad de Buenos Aires | ||
| 536 | |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas | ||
| 536 | |a Detalles de la financiación: Facultad de Ciencias Físicas y Matemáticas | ||
| 536 | |a Detalles de la financiación: Instituto Nacional de Investigación Agropecuaria | ||
| 536 | |a Detalles de la financiación: Consejo Nacional de Investigaciones Científicas y Técnicas | ||
| 536 | |a Detalles de la financiación: U.S. Environmental Protection Agency | ||
| 536 | |a Detalles de la financiación: Office of Research and Development | ||
| 536 | |a Detalles de la financiación: U.S. Environmental Protection Agency, EPA | ||
| 536 | |a Detalles de la financiación: Health Canada | ||
| 536 | |a Detalles de la financiación: 1Laboratorio de Toxicología de Mezclas Químicas, Instituto de Investigación IQUIBICEN, Consejo Nacional de Investigaciones Científicas y Técnicas (CONICET), Departamento Química Biológica, Facultad de Ciencias Exactas y Naturales, Universidad de Buenos Aires, Ciudad Universitaria UBA, Ciudad Autónoma de Buenos Aires, Argentina 2National Exposure Research Laboratory (NERL), U.S. Environmental Protection Agency, Research Triangle Park, North Carolina, USA | ||
| 536 | |a Detalles de la financiación: The U.S. Environmental Protection Agency through its Office of Research and Development reviewed and approved this publication. However, it may not necessarily reflect official agency policy, and reference to commercial products or services does not constitute endorsement. The authors express their gratitude to Drs. Anna B. Lowitt, Michael F. Hughes, and Elin Ulrich for their comments on an earlier version of this article, and Dr. Kevin M. Crofton for his kind and highly valued guidance before and during the construction of this work. | ||
| 536 | |a Detalles de la financiación: additional lab assays be conducted under specific guidelines to consider potential health risks in humans. Such guidelines are elaborated and enforced by authorities responsible for ensuring validity, adequacy, and sufficiency of lab data packet (Health Canada, 2009; U.S. Environmental Protection Agency [EPA], 2012a, 2013; Organization for Economic Cooperation and Development [OECD], 2012). | ||
| 593 | |a Laboratorio de Toxicología de Mezclas Químicas, Departamento Química Biológica, Universidad de Buenos Aires, (UBA), Piso 4, Pabellón 2, Ciudad Autónoma de Buenos Aires (1428EGA), Argentina | ||
| 593 | |a National Exposure Research Laboratory (NERL), U.S. Environmental Protection Agency, Research Triangle Park, NC, United States | ||
| 690 | 1 | 0 | |a ALLETHRIN |
| 690 | 1 | 0 | |a BIOALLETHRIN |
| 690 | 1 | 0 | |a CYFLUTHRIN |
| 690 | 1 | 0 | |a PHENOTHRIN |
| 690 | 1 | 0 | |a PYRETHROID |
| 690 | 1 | 0 | |a RESMETHRIN |
| 690 | 1 | 0 | |a TETRAMETHRIN |
| 690 | 1 | 0 | |a TRALOMETHRIN |
| 690 | 1 | 0 | |a PYRETHROID |
| 690 | 1 | 0 | |a ABSORPTION |
| 690 | 1 | 0 | |a AGE |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a CHEMICAL SAFETY |
| 690 | 1 | 0 | |a CHEMICAL STRUCTURE |
| 690 | 1 | 0 | |a CIRCADIAN RHYTHM |
| 690 | 1 | 0 | |a DRUG EXPOSURE |
| 690 | 1 | 0 | |a ENVIRONMENTAL MONITORING |
| 690 | 1 | 0 | |a ENVIRONMENTAL TEMPERATURE |
| 690 | 1 | 0 | |a HEALTH STATUS |
| 690 | 1 | 0 | |a HUMAN |
| 690 | 1 | 0 | |a LC 50 |
| 690 | 1 | 0 | |a LETHAL DOSE |
| 690 | 1 | 0 | |a LETHALITY |
| 690 | 1 | 0 | |a MOTOR ACTIVITY |
| 690 | 1 | 0 | |a NEUROTOXICITY |
| 690 | 1 | 0 | |a NEUROTOXICOLOGY |
| 690 | 1 | 0 | |a NONHUMAN |
| 690 | 1 | 0 | |a NONTARGET ORGANISM |
| 690 | 1 | 0 | |a PHOTODEGRADATION |
| 690 | 1 | 0 | |a QUANTITATIVE STRUCTURE PROPERTY RELATION |
| 690 | 1 | 0 | |a RISK ASSESSMENT |
| 690 | 1 | 0 | |a ROOM TEMPERATURE |
| 690 | 1 | 0 | |a SPECIES |
| 690 | 1 | 0 | |a STEREOCHEMISTRY |
| 690 | 1 | 0 | |a TARGET ORGAN |
| 690 | 1 | 0 | |a TARGET ORGANISM |
| 690 | 1 | 0 | |a TASK PERFORMANCE |
| 690 | 1 | 0 | |a TOXICITY TESTING |
| 690 | 1 | 0 | |a TOXICOKINETICS |
| 690 | 1 | 0 | |a XENOBIOTIC METABOLISM |
| 690 | 1 | 0 | |a ANIMAL |
| 690 | 1 | 0 | |a DISEASE MODEL |
| 690 | 1 | 0 | |a DOSE RESPONSE |
| 690 | 1 | 0 | |a ENVIRONMENTAL MONITORING |
| 690 | 1 | 0 | |a METHODOLOGY |
| 690 | 1 | 0 | |a REVIEW |
| 690 | 1 | 0 | |a TOXICITY AND INTOXICATION |
| 690 | 1 | 0 | |a NEUROTOXICITY SYNDROMES |
| 690 | 1 | 0 | |a PROCEDURES |
| 690 | 1 | 0 | |a TOXICITY |
| 690 | 1 | 0 | |a ANIMALS |
| 690 | 1 | 0 | |a DISEASE MODELS, ANIMAL |
| 690 | 1 | 0 | |a DOSE-RESPONSE RELATIONSHIP, DRUG |
| 690 | 1 | 0 | |a ENVIRONMENTAL MONITORING |
| 690 | 1 | 0 | |a NEUROTOXICITY SYNDROMES |
| 690 | 1 | 0 | |a PYRETHRINS |
| 690 | 1 | 0 | |a ANIMALS |
| 690 | 1 | 0 | |a DISEASE MODELS, ANIMAL |
| 690 | 1 | 0 | |a DOSE-RESPONSE RELATIONSHIP, DRUG |
| 690 | 1 | 0 | |a ENVIRONMENTAL MONITORING |
| 690 | 1 | 0 | |a NEUROTOXICITY SYNDROMES |
| 690 | 1 | 0 | |a PYRETHRINS |
| 700 | 1 | |a Tornero-Velez, R. | |
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