Developmental toxicity studies on triclopyr acid, triclopyr butoxyethyl ester and triclopyr triethylamine salt in the rabbit.

Developmental toxicity studies have been conducted in the rabbit on triclopyr acid and its active-ingredient variants, triclopyr triethylamine salt (T-TEA) and triclopyr butoxyethyl ester (T-BEE), which are dissociated or hydrolysed in vivo to triclopyr acid. In this paper, the available developmental toxicity studies on triclopyr acid, T-TEA and T-BEE are summarised and evaluated. For triclopyr acid and T-TEA, there was no evidence of impaired reproductive performance, fetotoxicity, or teratogenicity, even at maternally toxic doses. The no-observed-adverse-effect levels (NOAELs) for developmental toxicity were 75 mg/kg bw per day for triclopyr acid and 100 mg/kg bw per day for T-TEA, equivalent to 72 mg/kg bw per day expressed as triclopyr acid. A study on T-BEE showed increased post-implantation loss and slight increases in skeletal anomalies and variants at the highest dose tested of 100 mg/kg bw per day, a maternally toxic dose. In a follow-up study on T-BEE, focusing on post-implantation loss, no general increase in post-implantation loss was observed, but one animal at 100 mg/kg bw per day with maternal toxicity had complete resorption of implants. The NOAEL for post-implantation loss was 60 mg/kg bw per day, equivalent to 44 mg/kg bw per day expressed as triclopyr acid. It cannot be excluded that T-BEE may be associated with increased post-implantation loss, but it was only seen in association with maternal toxicity. It is concluded that triclopyr acid and its variants are not specifically toxic to the rabbit embryo and fetus, since post-implantation loss only occurred at doses causing maternal toxicity.

Reproductive and developmental evaluations of triclopyr acid, triclopyr butoxyethyl ester and triclopyr triethylamine salt in the rat.

Reproductive and developmental toxicity studies have been conducted in rat and rabbit on triclopyr acid and its active-ingredient variants, triclopyr butoxyethyl ester (T-BEE) and triclopyr triethylamine salt (T-TEA). In this paper the results of a rat two-generation study on triclopyr acid are presented, together with a review of all the reproductive and developmental toxicity data available from the rat studies. In the rat two-generation study, triclopyr acid was administered in the diet, giving doses of 0, 5, 25 or 250 mg/kg bw per day. Parental toxicity, especially maternal toxicity, occurred at 250 mg/kg bw per day with reduced body weight and feed intake, organ weight changes, and kidney toxicity. Slight kidney toxicity was also evident at 25 mg/kg bw per day. Developmental toxicity, in the form of reduced postnatal survival in the F1 and F2 generations and reductions in pre-weaning offspring body weight in both generations, was seen only at a dose causing significant parental toxicity. There were no effects on any other reproductive or developmental parameters at any dose. It is concluded that the developmental toxicity, seen only at the highest dose, was most likely attributable to maternal toxicity. The no-observed-adverse-effect levels were 5 mg/kg bw per day for parental toxicity and 25 mg/kg bw per day for developmental toxicity. From the multigeneration and developmental toxicity studies on triclopyr and its variants, it can also be concluded that triclopyr is not specifically toxic to reproduction and is not selectively toxic to the embryo, fetus or neonate in the rat.

Thresholds of Toxicological Concern for cosmetics-related substances: New database, thresholds, and enrichment of chemical space.

A new dataset of cosmetics-related chemicals for the Threshold of Toxicological Concern (TTC) approach has been compiled, comprising 552 chemicals with 219, 40, and 293 chemicals in Cramer Classes I, II, and III, respectively. Data were integrated and curated to create a database of No-/Lowest-Observed-Adverse-Effect Level (NOAEL/LOAEL) values, from which the final COSMOS TTC dataset was developed. Criteria for study inclusion and NOAEL decisions were defined, and rigorous quality control was performed for study details and assignment of Cramer classes. From the final COSMOS TTC dataset, human exposure thresholds of 42 and 7.9 µg/kg-bw/day were derived for Cramer Classes I and III, respectively. The size of Cramer Class II was insufficient for derivation of a TTC value. The COSMOS TTC dataset was then federated with the dataset of Munro and colleagues, previously published in 1996, after updating the latter using the quality control processes for this project. This federated dataset expands the chemical space and provides more robust thresholds. The 966 substances in the federated database comprise 245, 49 and 672 chemicals in Cramer Classes I, II and III, respectively. The corresponding TTC values of 46, 6.2 and 2.3 µg/kg-bw/day are broadly similar to those of the original Munro dataset.

Racemic versus enantiopure alanine on Cu(110): an experimental study.

The adsorption of racemic alanine on the Cu(110) surface has been compared to that of enantiopure alanine using low-energy electron diffraction (LEED), reflection absorption infrared spectroscopy (RAIRS), and scanning tunneling microscopy (STM). No evidence of chiral resolution at the surface was observed for the racemic system, indicating that the formation of separate enantiopure areas is not preferred. Also, in contrast to the enantiopure system, no chirally organized phase was observed for the racemic system. LEED shows that both systems display a common (3 x 2) phase at high coverage. However, the pathway and kinetic barriers to this phase differ markedly for the racemic and the enantiopure systems, with the racemic (3 x 2) appearing at a temperature that is more than 100 K below that required for the enantiopure system. In addition, we report intriguing complexities for the (3 x 2) LEED structure that is ubiquitous in amino acid/Cu(110) systems. First, a common (3 x 2) pattern with a zigzag distortion can be associated with both the racemic and enantiopure systems. For the racemic system, the coverage can be increased further to give a "true" (3 x 2) LEED pattern, which is a transformation that is impossible to enact for the enantiopure system. Most importantly, STM images of the "distorted" and "true" (3 x 2) structures created in the racemic system show subtle differences with neither arrangement being fully periodic over distances greater than a few molecules. Thus, the (3 x 2) phase appears to be more complicated than at first indicated and will require more complex models for a full interpretation.

Agricultural chemicals and endocrine-mediated chronic toxicity or carcinogenicity.

This brief review summarizes information on the endocrine effects and mechanisms of action of certain pesticides and considers whether exposure to pesticides with endocrine activity may play a role in human endocrine-related tumors of the breast, testis, prostate, and endometrium. Both animal and human data are considered. If animal data are to be used effectively for predicting human risk, a thorough understanding of comparative endocrinology and the underlying endocrine and pathological mechanisms contained in the animal model is needed. It is concluded that the evidence does not support an association between organochlorine pesticides and breast cancer, while the evidence on other tumor sites is too sparse to draw any conclusions concerning pesticides.

Supramolecular assembly of strongly chemisorbed size- and shape-defined chiral clusters: S- and R-alanine on Cu(110).

The bonding and self-assembly of a chirally organized monolayer of alanine on the Cu(110) surface has been investigated using reflection-absorption infrared spectroscopy, low-energy electron diffraction (LEED), and scanning tunneling microscopy (STM). This multitechnique approach has enabled an in-depth understanding of the hierarchy of chirality transfer: from a single adsorbed molecule, to size-defined chiral clusters, and then to an overall chiral assembly. The data have indicated that the alanine is in its anionic form, bound to the copper surface through the oxygens of the ionized carboxylate group and the nitrogen of the neutral amino group. Importantly, the methyl group is held away from the surface, resulting in direct chirality transfer into the footprint of the adsorbed alanine molecules, with the local adsorption motif for S-alanine being the mirror image of that created for R-alanine. STM has shown that S-alanine molecules self-organize to form size-defined chiral clusters of six or eight molecules at the surface, interspersed with chiral channels of bare metal. Together, these clusters and channels further self-assemble into a chiral array with one unique chiral domain sustained across the entire surface. A similar chiral assembly, but with the mirror organization, has been observed for R-alanine. Structural models for the individual clusters are proposed, and in conjunction with LEED data, overall models for these chiral phases of both S- and R-alanine have been constructed. Overall, this adsorption system has been found to be both strongly chemisorbed and capable of extensive intermolecular H-bonding, causing stresses that lead not only to the chiral self-organization of molecules but also to a specific self-organization of the empty chiral channels and spaces that intersperse the structure which, in turn, chirally assemble across macroscopic length scales to give a surface with global organizational chirality.