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1.
Environ Mol Mutagen ; 58(5): 325-344, 2017 06.
Article in English | MEDLINE | ID: mdl-28329407

ABSTRACT

Active ingredients in plant protection products are subject to rigorous safety assessment during their development, including assessment of genotoxicity. Plant protection products are used for agriculture in multiple regions and for the registration of active ingredients it is necessary to satisfy the data requirements of these different regions. There are no overarching global agreements on which genotoxicity studies need to be conducted to satisfy the majority of regulatory authorities. The implementation of new OECD guidelines for the in vitro micronucleus, transgenic rodent somatic and germ cell gene mutation and in vivo comet assays, as well as the revision of a number of other OECD test guidelines has resulted in some changes to data requirements. This review describes the genotoxicity data requirements for chemical active ingredients as well as biologicals, microbials, ground water metabolites, metabolites, and impurities in a number of regions. Similarities and differences are highlighted. Environ. Mol. Mutagen. 58:325-344, 2017. © 2017 Wiley Periodicals, Inc.


Subject(s)
Agrochemicals/toxicity , Mutagenicity Tests/methods , Animals , Comet Assay , Humans
2.
Regul Toxicol Pharmacol ; 83: 109-116, 2017 Feb.
Article in English | MEDLINE | ID: mdl-27871869

ABSTRACT

This paper describes the further development of a read-across approach applicable to the toxicological assessment of structurally-related xenobiotic metabolites. The approach, which can be applied in the absence of definitive identification of all the individual metabolites, draws on the use of chemical descriptors and multi-variate statistical analysis to define a composite "chemical space" and to classify and characterize closely-related subgroups within this. In this example, consideration of the descriptors driving grouping, combined with empirical evidence for lack of significant further biotransformation of metabolites, leads to the conclusion that, in the absence of any specific structural alerts, the relative toxicity of metabolites within a single grouping will be determined by their relative systemic exposure as described by their ADME characteristics. The in vivo testing of a smaller number of exemplars, selected to have representative ADME properties for each grouping, is sufficient, therefore, to evaluate the toxicity of the remainder. The approach is exemplified using the metabolites of the herbicide S-metolachlor, detected in the leachate of a soil lysimeter.


Subject(s)
Acetamides/toxicity , Environmental Monitoring/instrumentation , Soil Pollutants/pharmacokinetics , Soil Pollutants/toxicity , Toxicity Tests/methods , Toxicokinetics , Xenobiotics/toxicity , Acetamides/chemistry , Acetamides/classification , Acetamides/pharmacokinetics , Animals , Biotransformation , Environmental Exposure/adverse effects , Environmental Monitoring/methods , Humans , Models, Chemical , Models, Statistical , Molecular Structure , Multivariate Analysis , Principal Component Analysis , Risk Assessment , Soil Pollutants/chemistry , Soil Pollutants/classification , Structure-Activity Relationship , Xenobiotics/chemistry , Xenobiotics/classification , Xenobiotics/pharmacokinetics
3.
Environ Toxicol Chem ; 35(6): 1401-12, 2016 06.
Article in English | MEDLINE | ID: mdl-26627902

ABSTRACT

Lysimeter studies can be used to identify and quantify soil degradates of agrochemicals (metabolites) that have the potential to leach to groundwater. However, the apparent metabolic profile of such lysimeter leachate samples will often be significantly more complex than would be expected in true groundwater samples. This is particularly true for S-metolachlor, which has an extremely complex metabolic pathway. Consequently, it was not practically possible to apply a conventional analytical approach to identify all metabolites in an S-metolachlor lysimeter study, because there was insufficient mass to enable the use of techniques such as nuclear magnetic resonance. Recent advances in high-resolution accurate mass spectrometry, however, allow innovative screening approaches to characterize leachate samples to a greater extent than previously possible. Leachate from the S-metolachlor study was screened for accurate masses (±5 ppm of the nominal mass) corresponding to more than 400 hypothetical metabolite structures. A refined list of plausible metabolites was constructed from these data to provide a comprehensive description of the most likely metabolites present. The properties of these metabolites were then evaluated using a principal component analysis model, based on molecular descriptors, to visualize the entire chemical space and to cluster the metabolites into a number of subclasses. This characterization and principal component analysis evaluation enabled the selection of suitable representative metabolites that were subsequently used as exemplars to assess the toxicological relevance of the leachate as a whole. Environ Toxicol Chem 2016;35:1401-1412. © 2015 SETAC.


Subject(s)
Acetamides/analysis , Agrochemicals/analysis , Groundwater/chemistry , Mass Spectrometry/methods , Soil , Water Pollutants, Chemical/analysis , Acetamides/chemistry , Agrochemicals/chemistry , Databases, Factual , Models, Theoretical , Principal Component Analysis , Sensitivity and Specificity , Soil/chemistry , Soil/standards , Water Pollutants, Chemical/chemistry
4.
J Am Chem Soc ; 125(3): 830-9, 2003 Jan 22.
Article in English | MEDLINE | ID: mdl-12526684

ABSTRACT

Atomic force microscopy has been used to image the various facets of two morphologically distinct samples of silicalite. The smaller (20 microm) sample A crystals show 1 nm high radial growth terraces. The larger (240 microm) sample B crystals show growth terraces 1 to 2 orders of magnitude higher than the terraces on sample A with growth edges parallel to the crystallographic axes. Moreover, the terraces on the (010) face are significantly higher than the terraces on the (100) face - inconsistent with the previously proposed 90 degrees intergrowth structure. Sample A highlights that under certain synthetic conditions, silicalite grows in a manner akin to zeolites Y and A, via the deposition of layers comprising, in the case of silicalite, pentasil chains. It is probable that the rate of terrace advance is identical on the (010) and (100) faces, and it is the rate of terrace nucleation that dictates the overall growth rate of each facet and hence the relative size expressed in the final crystal morphology. Analysis of the growth terraces of sample B and detailed consideration of the structures of both MFI, and a closely related material MEL, lead to the proposal of a generalized growth mechanism for silicalite including the incorporation of defects within the structure. These defects are thought to be responsible for both the relative and the absolute terrace heights observed and may also explain the hourglass phenomenon observed by optical microscopy. The implications of this growth mechanism, supported by results of infrared microscopy, generate a new dimension to the continuing debate on the existence of intergrowths within one of the most important structures relevant to zeolite catalysis.

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