Your browser doesn't support javascript.
loading
Mostrar: 20 | 50 | 100
Resultados 1 - 2 de 2
Filtrar
Mais filtros










Base de dados
Intervalo de ano de publicação
1.
Mutat Res ; 521(1-2): 121-35, 2002 Nov 26.
Artigo em Inglês | MEDLINE | ID: mdl-12438010

RESUMO

Recent advances in genetic toxicity (mutagenicity) testing methods and in approaches to performing risk assessment are prompting a renewed effort to harmonize genotoxicity risk assessment across the world. The US Environmental Protection Agency (EPA) first published Guidelines for Mutagenicity Risk Assessment in 1986 that focused mainly on transmissible germ cell genetic risk. Somatic cell genetic risk has also been a risk consideration, usually in support of carcinogenicity assessments. EPA and other international regulatory bodies have published mutagenicity testing requirements for agents (pesticides, pharmaceuticals, etc.) to generate data for use in genotoxicity risk assessments. The scheme that follows provides a proposed harmonization approach in which genotoxicity assessments are fully developed within the risk assessment paradigm used by EPA, and sets out a process that integrates newer thinking in testing battery design with the risk assessment process. A classification strategy for agents based on inherent genotoxicity, dose-responses observed in the data, and an exposure analysis is proposed. The classification leads to an initial level of concern for genotoxic risk to humans. A total risk characterization is performed using all relevant toxicity data and a comprehensive exposure evaluation in association with the genotoxicity data. The result of this characterization is ultimately used to generate a final level of concern for genotoxic risk to humans. The final level of concern and characterized genotoxicity risk assessment are communicated to decision makers for possible regulatory action(s) and to the public.


Assuntos
Testes de Mutagenicidade/métodos , Medição de Risco , Animais , Bactérias/efeitos dos fármacos , Bactérias/genética , Relação Dose-Resposta a Droga , Guias como Assunto , Camundongos , Testes para Micronúcleos , Estados Unidos , United States Environmental Protection Agency/normas
2.
Mutat Res ; 512(1): 1-35, 2002 Sep.
Artigo em Inglês | MEDLINE | ID: mdl-12220588

RESUMO

The known aneuploidogens, benomyl and its metabolite, carbendazim (methyl 2-benzimidazole carbamate (MBC)), were selected for the third in a series of ongoing projects with selected pesticides. Mutagenicity and carcinogenicity data submitted to the US Environmental Protection Agency's (US EPA's) Office of Pesticide Programs (OPP) as part of the registration process are examined along with data from the open literature. Mutagenicity and carcinogenicity profiles are developed to provide a complete overview and to determine whether an association can be made between benomyl- and MBC-induced mouse liver tumors and aneuploidy. Since aneuploidogens are considered to indirectly affect DNA, the framework adopted by the Agency for evaluating any mode of action (MOA) for carcinogenesis is applied to the benomyl/MBC data. Both agents displayed consistent, positive results for aneuploidy induction but mostly negative results for gene mutations. Non-linear dose responses were seen both in vitro and in vivo for aneuploidy endpoints. No evidence was found suggesting that an alternative MOA other than aneuploidy may be operative. The data show that by 14 days of benomyl treatment, events associated with liver toxicity appear to set in motion the sequence of actions that leads to neoplasms. Genetic changes (as indicated by spindle impairment leading to missegregation of chromosomes, micronucleus induction and subsequent aneuploidy in bone marrow cells) can commence within 1-24h after dosing, well within the time frame for early key events. Critical steps associated with frank tumor formation in the mouse liver include hepatotoxicity, increased liver weights, cell proliferation, hypertrophy, and other steps involving hepatocellular alteration and eventual progression to neoplasms. The analysis, however, reveals weaknesses in the data base for both agents (i.e. no studies on mouse tubulin binding, no in vivo assays of aneuploidy on the target tissue (liver), and no clear data on cell proliferation relative to dose response and time dependency). The deficiencies in defining the MOA for benomyl/MBC introduce uncertainties into the analysis; consequently, benomyl/MBC induction of aneuploidy cannot be definitively linked to mouse liver carcinogenicity at this time.


Assuntos
Benomilo/toxicidade , Benzimidazóis/toxicidade , Carbamatos , Fungicidas Industriais/toxicidade , Herbicidas/toxicidade , Animais , Benomilo/farmacocinética , Benzimidazóis/farmacocinética , Biotransformação , Células CHO/efeitos dos fármacos , Testes de Carcinogenicidade , Carcinoma/induzido quimicamente , Cricetinae , Cricetulus , Reparo do DNA/efeitos dos fármacos , Relação Dose-Resposta a Droga , Feminino , Fungicidas Industriais/farmacocinética , Herbicidas/farmacocinética , Humanos , Leucemia L5178/patologia , Neoplasias Hepáticas Experimentais/induzido quimicamente , Camundongos , Camundongos Endogâmicos , Testes de Mutagenicidade , Saccharomyces cerevisiae/efeitos dos fármacos , Salmonella typhimurium/efeitos dos fármacos , Troca de Cromátide Irmã/efeitos dos fármacos , Células Tumorais Cultivadas/efeitos dos fármacos
SELEÇÃO DE REFERÊNCIAS
DETALHE DA PESQUISA
...