Mixture risk assessment: a case study of Monsanto experiences.

Monsanto employs several pragmatic approaches for evaluating the toxicity of mixtures. These approaches are similar to those recommended by many national and international agencies. When conducting hazard and risk assessments, priority is always given to using data collected directly on the mixture of concern. To provide an example of the first tier of evaluation, actual data on acute respiratory irritation studies on mixtures were evaluated to determine whether the principle of additivity was applicable to the mixture evaluated. If actual data on the mixture are unavailable, extrapolation across similar mixtures is considered. Because many formulations are quite similar in composition, the toxicity data from one mixture can be extended to a closely related mixture in a scientifically justifiable manner. An example of a family of products where such extrapolations have been made is presented to exemplify this second approach. Lastly, if data on similar mixtures are unavailable, data on component fractions are used to predict the toxicity of the mixture. In this third approach, process knowledge and scientific judgement are used to determine how the known toxicological properties of the individual fractions affect toxicity of the mixture. Three examples of plant effluents where toxicological data on fractions were used to predict the toxicity of the mixture are discussed. The results of the analysis are used to discuss the predictive value of each of the above mentioned toxicological approaches for evaluating chemical mixtures.

Evaluation of a method used to test for potential toxicity of carpet emissions.

After a private testing laboratory had reported mortality, neurotoxicity, and respiratory irritation in mice exposed to emissions from heated carpet in a modified application of the sensory irritation test (ASTM E981-84), the studies reported in this paper were conducted to evaluate the method used in testing for carpet toxicity and to see if the reported findings were reproducible. Mice were exposed head-only to offgasses generated by heating carpet (AT #3) to temperatures that ranged from 37 to 70 degrees C. Control mice were simultaneously exposed to heated air. The animals were evaluated for mortality, clinical signs and respiratory irritation. Neurotoxicity was evaluated using functional observational battery and motor activity monitoring. Pathological evaluations of organs and tissues, including the nervous system, were also conducted. The carpet samples heated to higher temperatures produced greater concentrations of total volatile organic compounds than those heated to 37 degrees C. Both carpet-exposed and control mice displayed some effects, such as body weight loss, mortality and pathological lesions, that were due to the exposure system. There was no mortality or neurotoxicity, nor were there clinical signs or pathological lesions as a result of carpet exposures. Mice exposed to carpet heated to 70 degrees C had slightly decreased respiratory rates and an increased incidence of breathing patterns indicative of sensory irritation. Therefore, none of the results reported by the private testing laboratory could be reproduced when this carpet was heated to temperatures below 70 degrees C, and slight sensory irritation was the only effect observed at the 70 degrees C test conditions. Effects from the exposure system itself made interpretation of results difficult, and concurrent controls were considered essential for interpretation of data.

Structure-activity relationship of a series of sensory irritants.

The relative potencies for a series of sensory irritants, with structures based on toluene, were determined by measuring the airborne concentrations that caused a 50% decrease in respiratory rate in Swiss-Webster mice. This concentration is referred to as the RD50. Toluene, a relatively nonirritating compound, and compounds with chlorine, two chlorines, bromine, and iodine atoms substituted on the alpha carbon of toluene were tested. The RD50s for these compound types were determined to be 4900, 27, 27, 5.2, and 4.3 ppm, respectively. In addition, compounds with chlorine substituted at the ortho, meta, and para positions on the toluene ring were also tested. The RD50s were determined to be 4.9, 13, and 14 ppm, respectively. The structure-activity relationships of the compounds studied are explained by a model (Abraham et al., 1990; Nielsen and Alarie, 1982) that relates the interaction of sensory irritants with a receptor protein in a lipid bilayer. The trends in the RD50s, and thus sensory irritation, for the compounds studies are related to the development of a partial positive charge on the toluene alpha carbon by the positioning of a ring chlorine and the bond dissociation energies of the alpha carbon-halogen bond for the iodo, bromo, and chloro isomers of benzyl halide.

Biochemical toxicology and disposition of Therminol 66 heat transfer fluid after inhalation or after dietary administration to male Sprague-Dawley rats.

The objectives of this study were to determine the disposition of Therminol 66 in rats and to determine the effects of this heat-transfer fluid on liver and kidney microsomal drug-metabolizing enzymes. Therminol 66 was administered to male Sprague-Dawley rats at various doses as either a single oral administration at 0, 100, or 300 mg/kg, or as a single 6-h inhalation exposure at 0 or 350 mg/m3. Animals were killed 48 h after gavage or after termination of inhalation exposure. Additional groups of animals were exposed to Therminol 66 via the diet at 0, 100, 500, or 5000 ppm for 14 d, or via repeated inhalation exposure at 0, 25, 250, or 1200 mg/m3 for 6 h/d for 14 d. These exposure scenarios represent approximately equivalent doses of Therminol 66 by the different routes of administration. No change in body weight was observed after acute oral or inhalation exposure, and little change in body weight was observed in animals administered Therminol 66 via the diet except at the highest dose. There was no change in kidney weight, and liver weights were increased only at the higher doses of Therminol 66. The body weight gain of animals exposed to Therminol 66 via inhalation decreased in a dose-dependent manner over the 2-wk exposure period. Results from the disposition study indicated that Therminol 66 did not appear to accumulate in the tissues examined and did not appear to be extensively absorbed after a single oral dose of 300 mg/kg. The whole-body elimination half-life was approximately 14 h and occurred primarily via the feces. There was no significant induction of hepatic aryl hydrocarbon hydroxylase (AHH) activity after single oral or inhalation exposures to Therminol 66. Ethoxycoumarin O-deethylase (ECOD) was significantly induced only in animals exposed to 350 mg/m3 via inhalation. Repeated dietary and inhalation exposures resulted in AHH and ECOD induction only at the highest doses, and the kidney appeared to be less sensitive than the liver. Animals exposed via inhalation demonstrated a greater hepatic inductive effect than did animals exposed via the diet, which may be due to absorption differences.(ABSTRACT TRUNCATED AT 400 WORDS)

Evidence for the existence of neurotoxic esterase in neural and lymphatic tissue of the adult hen.

Hen brain and spinal cord contain a number of esterases that hydrolyze phenyl valerate (PV). Most of this activity is sensitive to inhibition by micromolar concentrations of paraoxon. Included among the paraoxon-resistant esterases is neurotoxic esterase (NTE), which is inhibited in vivo and in vitro by certain organophosphorus compounds, such as mipafox, which cause delayed neurotoxicity. Since published information on the NTE content of non-neural tissues was heretofore lacking, a comprehensive study was undertaken of the occurrence of this enzyme in tissues of the adult hen (Gallus gallus domesticus), the species of choice in the study of organophosphorus-induced delayed neurotoxicity. Complete differential titration curves of PV esterase activity were obtained by preincubation of each tissue homogenate with a wide range of concentrations of paraoxon, a non-neurotoxic compound, plus or minus mipafox, a neurotoxic compound, followed by PV esterase assay. Brain NTE activity was determined to be 2426 +/- 104 nmoles.min-1.(g wet weight)-1 (mean +/- S.E.M.). Titration of other tissues resulted in the following NTE activities, expressed as percentages of brain NTE activity: spinal cord (21%), peripheral nerve (1.7%), gastrocnemius muscle (0%), pectoralis muscle (0%), heart (4%), liver (0%), kidney (0%), spleen (70%), spleen lymphocytes (26%), and blood lymphocytes (24%). Using an abbreviated procedure, erythrocytes and plasma showed no NTE activity. These results indicate that NTE has limited distribution among the tissues of the adult hen and is present in lymphatic as well as neural tissue.