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The contribution of acute toxicity in animals to occupational exposure limits of chemical substances.

The correlations of lethal doses of various industrial chemicals for rats and mice with occupational exposure limit values were investigated. 50% lethal dose (LD50) values obtained by oral (p.o.) and intraperitoneal (i.p.) injection and 50% lethal concentration (LC50) values obtained by inhalation exposure were collected from Registry of Toxic Effects of Chemical Substances (RTECS). Threshold Limit Value (Time-Weighted Average) (TLVs-TWA) and Threshold Limit Value (Short Term Exposure Limit) (TLVs-STEL) recommended by American Conference of Governmental Industrial Hygienists (ACGIH) were used as exposure limits. TLVs-TWA or TLVs-STEL and LD50 or LC50 values obtained for the rats were plotted on logarithmic scales on the ordinate and abscissa, respectively. High correlations were obtained between these parameters. The order of correlations was: TLVs-STEL vs. LC50s > TLVs-TWA vs. LC50s > TLVs-TWA vs. LD50s i.p. > TLVs vs. LD50s p.o. The same calculations for the relationship between TLVs and lethal doses in mice were also performed. The order of the three types of correlations was same as that of the rats; however, correlation coefficients for TLVs-STEL vs. LC50s and for TLVs-TWA vs. LC50s obtained in mice were smaller than those in rats. TLVs-TWA are, therefore, well correlated with LC50 values rather than LD50 values, particularly with those in rats. High correlations between TLVs-STEL vs. LC50s were also obtained, as had been expected before calculation. The equation: TLV-TWA = 10b x (LC50)a can be obtained from these plottings, where the values a and b are taken from each linear regression line. TLV-TWA for each chemical can be calculated by using LC50 and the equation. The upper and lower 95% confidence limits for calculated TLV-TWA were TLV-TWA (calculated from LC50) x 22.9 and TLV-TWA (calculated)/22.9, respectively, where LC50 for rats expressed in ppm x hr was used.

Animals↗

Effect of exposure of pregnant rats to cadmium on prenatal and postnatal development of the young.

Cadmium chloride in doses of 2, 12 and 40 mg Cd/kg was administered per os to pregnant rats from the 7th to 16th day of pregnancy. In another experiment female rats were exposed to cadmium oxide at a concentration of 0.02 mg Cd/m3 or 0.16 mg Cd/m3 for 5 hours a day and 5 days weekly for a period of 5 months or 1 mg Cd/m3 for 4 months. The exposure was then continued during mating and from the 1st to 20th day of pregnancy. A decrease in fertility was only observed in females exposed by inhalation to cadmium oxide at a concentration of 1 mg Cd/m3, at which concentration cadmium exhibits a considerable toxic effect on the whole organism. The young of females orally treated with CdCl2 in a dose of 40 mg Cd/kg displayed congenital defects in the form of sirenomelia or amelia, as well as raised cadmium levels in tissues. A retardation of intrauterine development manifested by lower body weight and slowed down osteogenesis was observed in the other groups. A cadmium concentration increase was not found in the tissues of the young in these groups. Inhalation exposure to 0.16 mg Cd/m3 of females prior to and during pregnancy induced in their young a decrease in viability, lower body weight gain, prolongation of latency in the negative-geotaxis test, lower locomotor activity and deteriorated development of the conditioned-reflex response. The offspring of females exposed to 0.02 mg Cd/m3 displayed lowered locomotor activity and worsened consolidation of the conditioned-reflex response.

Animals↗

Developmental toxicity of dimethyl sulfate by inhalation in the rat.

Dimethyl sulfate (DMS; CAS No. 77-78) is a colorless, oily liquid which is used as a chemical intermediate and as a reactant in producing polyurethane resins. In this study, groups of pregnant Crl:CD BR rats were exposed, nose-only, to either 0.1, 0.7 or 1.5 ppm DMS by inhalation for 6 hr/day from Days 7 through 16 of gestation (day in which copulation plug was detected was designated Day 1G). A control group of pregnant rats was exposed simultaneously to air only. All female rats were euthanized on Day 22G and the fetuses were examined. A suppression of both food consumption and the rate of body weight gain was seen in the 0.7 and 1.5 ppm groups. No unusual clinical signs were seen in rats exposed to DMS. None of the reproductive parameters was altered in any of the groups and no statistically significant fetal effects were detected. DMS is not a developmental toxin in the rat following inhalation exposures up to 1.5 ppm during the period of major organogenesis.

Administration, Inhalation↗

Testing of selected workplace chemicals for teratogenic potential.

The reproductive toxicity and teratogenic potential of 19 industrial chemicals have been investigated during the past 3 a. Preliminary studies utilizing intraperitoneal treatments of rats on days 1-15 of gestation have been conducted on the following ten chemicals: allyl chloride, bisphenol A, copper naphthenate, ethylene dibromide, hexachlorobutadiene, 2-mercaptobenzothiazole, methyl styrene, naphthalene, 2-nitropropane, and 1,2,3-trichloropropane. Studies utilizing inhalation exposure of rats and rabbits on days 1-19 and 1-24, respectively, of gestation have been conducted on the following nine chemicals: butylene oxide, carbon disulfide, 2-ethoxyethanol, ethyl benzene, methyl bromide, nitrous oxide, styrene oxide, tetrachloroethylene, and trichloroethylene. In the preliminary studies, evidence of teratogenic potential was seen with allyl chloride and bisphenol A, and fetal toxicity was found in the absence of maternal toxicity with methyl styrene and 2-nitropropane. In the inhalation studies, 2-ethoxyethanol was strongly embryotoxic at the higher exposure levels employed and was teratogenic at the lower concentration.

Abnormalities, Drug-Induced↗

More precise localization of nasal tumors associated with chronic exposure of F-344 rats to formaldehyde gas.

Considerable interest and research have resulted from the finding that squamous cell carcinomas, polypoid adenomas, and a small number of other nasal neoplasms occurred in F-344 rats following chronic inhalation exposure to formaldehyde. These tumors were reported to originate in the anterior portion of the nasal cavity but their precise location in the nose was not determined. Histologic sections from the nasal passages of these rats have been reexamined and the location of each tumor has been recorded. The majority of squamous cell carcinomas occurred on the anterior portion of the lateral aspect of the nasoturbinate and adjacent lateral wall (57%) or the midventral nasal septum (26%). Polypoid adenomas were confined to a small region of the anterior nasal cavity and were restricted to the free margins of the naso-and maxilloturbinates and lateral wall adjacent to these margins. One neoplasm, considered to be the malignant counterpart of the polypoid adenoma, originated on the dorsal margin of the maxilloturbinate in the same region of the nose. Remaining neoplasms were generally too large or too poorly preserved for assessment of their site of origin. Mechanistic studies directed toward a better understanding of the nasal carcinogenicity of formaldehyde, or other nasal carcinogens. should take into account the anatomic sites of origin of the neoplasms whenever this can be determined.

Animals↗

Interim recommendations for protecting workers from exposure to Bacillus anthracis in work sites in which mail is handled or processed.

CDC has developed interim recommendations to assist personnel responsible for occupational health and safety in developing a comprehensive program to reduce potential cutaneous or inhalational exposures to Bacillus anthracis spores among workers in work sites in which mail is handled or processed. Such work sites include post offices, mail distribution/handling centers, bulk mail centers, air mail facilities, priority mail processing centers, public and private mail rooms, and other settings in which workers are responsible for handling and processing mail. The recommendations are based on the limited information available on methods to avoid infection and on the effectiveness of various prevention strategies. These recommendations will be updated as new informat on becomes available.

Anthrax↗

Characterization of a hooded human exposure apparatus for inhalation of gases and aerosols.

A human exposure apparatus was designed to administer a gas and/or aerosol directly to the subject's face. This apparatus utilized a hood associated with a powered air-purifying respirator. The design criteria included the need to maximize subject comfort, maintain consistent atmospheres of a gas or dust within the hood, and the accurate use of direct-reading instruments to monitor exposure levels. An 83-L drum was used to pre-mix the gas or aerosol with the main dilution air prior to entering the hood worn by the subject. A clear plastic oxygen tent, ventilated with room exhaust air, was used to contain contaminants exiting the hood. Bypass valves were added to allow for a startup period during which contaminant concentration levels were allowed to stabilize prior to exposing the human subject. Results from characterization studies demonstrated that the system adequately contained contaminants within the oxygen tent, provided adequate mixing of contaminant and dilution air, produced stable contaminant concentrations over time, and was responsive to sudden changes in contaminant generation rate.

Aerosols↗

Toxicology of 1,3-butadiene, chloroprene, and isoprene.

The diene monomers, 1,3-butadiene, chloroprene, and isoprene, respectively, differ only in substitution of a hydrogen, a chlorine, or a methyl group at the second of the four unsaturated carbon atoms in these linear molecules. Literature reviewed in the preceding sections indicates that these chemicals have important uses in synthesis of polymers, which offer significant benefits within modern society. Additionally, studies document that these monomers can increase the tumor formation rate in various organs of rats and mice during chronic cancer bioassays. The extent of tumor formation versus animal exposure to these monomers varies significantly across species, as well among strains within species. These studies approach, but do not resolve, important questions of human risk from inhalation exposure. Each of these diene monomers can be activated to electrophilic epoxide metabolites through microsomal oxidation reactions in mammals. These epoxide metabolites are genotoxic through reactions with nucleic acids. Some of these reactions cause mutations and subsequent cancers, as noted in animal experiments. Significant differences exist among the compounds, particularly in the extent of formation of highly mutagenic diepoxide metabolites, when animals are exposed. These metabolites are detoxified through hydrolysis by epoxide hydrolase enzymes and through conjugation with glutathione with the aid of glutathione S-transferase. Different strains and species perform these reactions with varying efficacy. Mice produce these electrophilic epoxides more rapidly and appear to have less adequate detoxification mechanisms than rats or humans. The weight of evidence from many studies suggests that the balance of activation versus detoxification offers explanation of differing sensitivities of animals to these carcinogenic actions. Other aspects, including molecular biology of the many processes that lead through specific mutations to cancer, are yet to be understood. Melnick and Sills (2001) compared the carcinogenic potentials of these three dienes, along with that of ethylene oxide, which also acts through an epoxide intermediate. From the number of tissue sites where experimental animal tumors were detected, butadiene offers greatest potential for carcinogenicity of these dienes. Chloroprene and then isoprene appear to follow in this order. Comparisons among these chemicals based on responses to external exposures are complicated by differences among studies and of species and tissue susceptibilities. Physiologically based pharmacokinetic models offer promise to overcome these impediments to interpretation. Mechanistic studies at the molecular level offer promise for understanding the relationships among electrophilic metabolites and vital genetic components. Significant improvements in minimization of industrial worker exposures to carcinogenic chemicals have been accomplished after realization that vinyl chloride caused hepatic angiosarcoma in polymer production workers (Creech and Johnson 1974; Falk et al. 1974). Efforts continue to minimize disease, particularly cancer, from exposures to chemicals such as these dienes. Industry has responded to significant challenges that affect the health of workers through efforts that minimize plant exposures and by sponsorship of research, including animal and epidemiological studies. Governmental agencies provide oversight and have developed facilities that accomplish studies of continuing scientific excellence. These entities grapple with differences in perspective, objectives, and interpretation as synthesis of knowledge develops through mutual work. A major challenge remains, however, in assessment of significance of environmental human exposures to these dienes. Such exposure levels are orders of magnitude less than exposures studied in experimental or epidemiological settings, but exposures may persist much longer and may involve unknown but potentially significant sensitivities in the general population. New paradigms likely will be needed for toxicological evaluation of these human exposures, which are ongoing but as yet are not interpreted.

Butadienes↗

Effects of trichloroethylene inhalation on proteins of the gerbil brain.

Inhalation exposure of adult Mongolian gerbils to 320 ppm of trichloroethylene (TCE) during 8 weeks causes a decrease of soluble proteins per wet weight in frontal cerebral cortex, cerebellar anterior part of the hemispheres and in the posterior part of vermis, as well as in hippocampus, although the levels of S 100, a glial cytoplasmic protein, showed an overgoing increase back to control levels, or a significant increase. In the sensory-motor cortex, an overgoing increase of soluble proteins, as well as of the S 100, were observed during the exposure period. One of the major soluble polypeptides (m.w. 50,000--52,000) of cerebral cortex, the cerebellar hemispheres and the brain stem, decreased at the end of the exposure period. Possible candidates for such a polypeptide are among others the subunit of microtubular protein or a subunit of (Na+K+)-ATPase. The results show that inhalation of TCE effect various brain areas differently. The observed biochemical changes could be interpreted as an adaptation and in some brain areas neuronal cells seem to be more sensitive than glial cells to TCE.

Animals↗

Concentration-dependent respiratory response of guinea pigs to paraquat aerosol.

Six groups of male English smooth-haired guinea pigs were exposed to a paraquat aerosol for 4 h. Concentrations of the paraquat ion aerosols ranged from 0.83 to 2.07 mg/m3. Over 85% of the particles in the aerosol were found to be under 0.65 micron. Tidal volume and respiratory frequency of each animal were measured prior to exposure, immediately following exposure, and 18 h following exposure. These parameters were monitored during air breathing and a 10% CO2 challenge using a whole body plethysmograph fitted with a head chamber. A concentration-related decrease in tidal volume and increase in respiratory frequency were found 18 h following exposure when breathing air and the CO2 mixture. Inspection of the flow-volume (V-VT) loops showed abnormal rectangular shapes 18 h following exposure, also varying with the concentration and indicative of lung restriction with a hyperventilation pattern. This study provides quantitative information on the respiratory toxicity following a paraquat inhalation exposure and qualitative description of its effect on the respiratory pattern. The measurements made may be of value in the search of antidotes for this important herbicide.

Aerosols↗

Assessment of risks in occupational cobalt exposures.

Exposure to cobalt can give rise to adverse health effects related to various organs or tissues, such as the respiratory organs, the skin, the hematopoietic tissues, the myocardium, the thyroid gland, as well as teratogenic and carcinogenic effects. In occupational and environmental health, it is important to identify effects that occur at relatively low exposure, i.e. the critical effects which are crucial for preventive action. The limited database available on cobalt toxicity makes it difficult to select critical effects. For dermal exposures, allergic dermatitis may be regarded as such an effect, even if this is a reversible condition and dose-response relationships need to be defined. For inhalation exposures, effects on the respiratory tract can be considered as critical effects. Evidence of cobalt carcinogenicity in humans is inadequate and cannot be evaluated quantitatively but an extra safety factor to be added on exposures estimated from other effects may well be needed. Risks for development of pneumoconiosis are likely to be dependent on physical and chemical characteristics of airborne cobalt containing particles, but such information is lacking in most studies. It has been recognised for many years that there is an excess risk of pneumoconiosis when exposure to cobalt containing dust exceeds 100 micrograms/m3. Recently considerably lower concentrations occurring in the cobalt diamond industry have given rise to such effects. Irritation of mucous membranes may occur at 5-10 micrograms/m3.

Animals↗

Assessment of genotoxic effects by lindane.

The well known and previously widespread insecticide lindane has been re-assessed for DNA-damaging activity. A first group of investigations using standard in vitro and in vivo mutagenicity assays did not indicate any genotoxic effects of lindane at all. The assay systems used were for the induction of HPRT mutations and sister chromatid exchanges in CHO cells cultured in vitro, and for micronuclei induction in vivo in bone marrow cells of rats, hamsters and mice. Also, lindane was assessed for its potential to induce sister chromatid exchanges in vivo in the bone marrow of Chinese hamsters. These specific assay systems had not been used previously for elucidating the genotoxic effects of this compound, but they are basically similar to other standard mutagenicity assays in which lindane has been shown to be devoid of genotoxic activity. The second part of the investigations was directed at re-evaluating a previously reported positive effect of the compound in primary rat hepatocytes in vitro. We performed in vitro and in vivo studies with hepatocytes from the rat liver and used alkaline elution to detect DNA damage. However, we could not demonstrate that lindane induced genotoxicity, unless considerable concomitant cytotoxicity was apparent as well. Finally, since lindane can be ingested and inhaled by humans, we also measured the induction of DNA damage in local target organs of absorption using single cell micro-gel-electrophoresis (the comet assay). In these cases lindane was genotoxic in cells of the gastric and nasal mucosa in vitro and also in vivo following appropriate routes of application (oral and inhalational exposure).

Administration, Inhalation↗

Spectrum of noninfectious health effects from molds.

Molds are eukaryotic (possessing a true nucleus) nonphotosynthetic organisms that flourish both indoors and outdoors. For humans, the link between mold exposure and asthma exacerbations, allergic rhinitis, infections, and toxicities from ingestion of mycotoxin-contaminated foods are well known. However, the cause-and-effect relationship between inhalational exposure to mold and other untoward health effects (eg, acute idiopathic pulmonary hemorrhage in infants and other illnesses and health complaints) requires additional investigation. Pediatricians play an important role in the education of families about mold, its adverse health effects, exposure prevention, and remediation procedures.

Child↗

[The cytogenetic activity of some brands of epoxy resins].

The studies have allow us to ascertain that some epoxy resins, such as DE-500, DE-1000, DE-2000, UP-650, UP-650T, under gastric administration at the dose levels of 1/10 and 1/50 DL50 (DL50 = 5338 +/- 1134, 6644 +/- 1114, 9180 +/- 1154, 7717 +/- 586, 6980 +/- 621 mg/kg for DE-500, DE-1000, DE-2000, UP-650, UP-650T respectively) and ED-22F under inhalational exposure at 1 mg/m3 as per epichlorhydrine over three to four months, have a striking effect on the chromosomal apparatus of the laboratory animals bone marrow cells, bringing about chromosomal structural aberrations. The cytogenetic activity was found to be dependent upon the dose employed as well as duration of the exposure and chemical structure of the epoxy resins.

Administration, Inhalation↗

Safety assessment of enzyme-containing personal cleansing products: exposure characterization and development of IgE antibody to enzymes after a 6-month use test.

BACKGROUND: Enzyme-containing personal cleansing products were being considered for the consumer market. Although enzymes have been marketed safely for many years as ingredients in laundry products, their use in a personal cleansing application represented a new type of exposure for consumers that was not supported by the historical safety data. An exposure assessment and additional safety data would be needed before marketing to ensure consumer safety. OBJECTIVE: The work in this paper was designed to evaluate the potential for inhalation exposure to the enzyme during use of this new product while showering. Then a clinical trial was conducted to determine whether or not the level, duration, and routes of exposure encountered during use of this product would induce a Type I sensitization response to the enzyme. METHODS: Exposure was assessed during normal showering activities by collecting air samples with both high volume and personal samplers and quantitating enzyme levels with an ELISA. To assess the potential for sensitization, panelists were asked to use a prototype protease-containing bar product for all personal cleansing tasks and to keep a use diary reporting any associated symptoms. Physical and dermatologic examinations and skin prick tests with enzyme were conducted before the test commenced and at 2-month intervals. RESULTS: Exposure assessment results showed that airborne enzyme levels were primarily dependent on the concentration of the enzyme in the personal cleansing product. Mean values for total airborne enzyme protein ranged from 5.7 to 11.8 ng/m3 when enzyme concentration, time of use, and measurement technique remained constant. After 6 months of at-home product use, four of 61 test subjects using the enzyme-containing bar had positive skin prick test responses when tested with the enzyme. The skin prick test data were supplemented with serologic analyses, which detected IgE specific for the protease enzyme. None of these subjects showed any clinical symptoms indicative of allergic reaction. CONCLUSION: The ability of enzymes to induce development of allergic antibodies in this study led to the conclusion that this prototype enzyme-containing personal cleansing bar would represent an inappropriate use of enzymes in a consumer product application. The likelihood of both induction of an immunologic response and subsequent elicitation of allergy symptoms in a small but significant fraction of the user population was high. This finding resulted in the decision to halt further development of this prototype.

Administration, Inhalation↗

An inhalation distribution model for the lactating mother and nursing child.

A rule-of-thumb methodology is presented to assist in assessing risk to a nursing child due to the mother's occupational inhalation exposure. The method represents an example of the use of physiologically based pharmacokinetic modeling using state-of-the-art computational techniques. A computer model is developed to describe distribution of non-metabolized, inhaled contaminants into a mother/child system as a function of the contaminant's blood:air and octanol:water partition coefficients. Risk is assessed in terms of the area under the blood concentration vs. time curve of the exposure chemical. Since low partition values yield low risk for the nursing child and high values yield high risk, the model is exercised over a range of intermediate values (blood:air = [2,25]; octanol:water = [100, 1500]). Results are thus applicable to chemicals for which the mother's dose is a strong factor in estimating the child's risk. The most notable observation is that, for the range of partition values used, this model never predicts a risk for the child greater than 25% of that of the mother. An equation is provided (based on model results) that expresses the child's risk as a fraction of the mother's risk.

Adult↗

PDE4 inhibition and a corticosteroid in chronically antigen exposed conscious guinea-pigs.

BACKGROUND: The physiological and pharmacological consequences of repeated aero-allergen challenge have not been previously characterized in conscious, sensitized guinea-pigs. OBJECTIVES: This study was undertaken to compare the effects of two anti-inflammatory compounds, dexamethasone and Ro 20- 1724, on an acute and chronic airway inflammation, in terms of airway function, reactivity and leucocyte infiltration. METHODS: Sensitized guinea-pigs received eight saline or ovalbumin (OvA) inhalation exposures over 4 weeks and either vehicle, the type 4 PDE inhibitor, Ro 20-1724 (3 mgkg(-1)), or dexamethasone (1.5 mg/kg(-1)), 30 min before and 6 h after each challenge. Airway function of the conscious animal (sGaw) was monitored over the duration of the first and final OvA challenge. Airway reactivity to the thromboxane mimetic, U46619, was also determined following the final OvA exposure as was the leucocyte infiltration. RESULTS: The first antigen challenge induced a large early (0-3h) and smaller late (17-24h) bronchoconstrictor response. Neither phase was affected by the drug treatments. The final OvA challenge induced early and late phase bronchoconstrictor responses but of similar magnitude. The late phase was also significantly prolonged. Ro 20-1724 and dexamethasone significantly attenuated both phases. Airway reactivity to the inhaled thromboxane mimetic, U46619, was also significantly enhanced at 120h after the final OvA exposure in contrast to the saline challenged group. This hyperreactivity was attenuated by Ro 20-1724 and dexamethasone. Bronchoalveolar lavage after repeated OvA exposures revealed eosinophilia which was attenuated by Ro 20-1724 and dexamethasone. CONCLUSIONS: This model demonstrates differential airway responses to acute and chronic antigen challenge. Repeated administration of dexamethasone and Ro 20-1724 with each OvA exposure attenuated all of the chronic inflammatory responses: early and late phase responses, hyperreactivity and eosinophilia.

15-Hydroxy-11 alpha,9 alpha-(epoxymethano)prosta-5↗

Respiratory hypersensitivity in guinea pigs sensitized to 1,6-hexamethylene diisocyanate (HDI): comparison of results obtained with the monomer and homopolymers of HDI.

This study used guinea pigs that were sensitized to the biuret or isocyanurate type homopolymers of 1,6 hexamethylene diisocyanate (HDI). Induction was either by intradermal injection or repeated inhalation exposures. For comparison, groups of guinea pigs were sensitized to monomeric HDI. Naive animals served as negative controls. Two and three weeks following induction, animals were challenged by inhalation with the hapten and homologous protein conjugate of the hapten, respectively. Assessments were based on changes in respiratory rate, serum IgG(1)-antibody titer, and influx of eosinophilic granulocytes in airways. Guinea pigs induced and challenged with the HDI-monomer did not display appreciable changes in respiratory rate, whilst the re-challenge with the HDI-protein conjugate caused unequivocal changes in respiratory patterns, including a marked bronchial influx of eosinophilic granulocytes. In contrast, animals induced and challenged with either the free or conjugated aerosols of HDI-homopolymers failed to elicit specific physiological or morphological pulmonary responses. IgG(1) antibodies were observed in all groups receiving monomeric HDI or HDI-homopolymers. Based on the comparative assessment of antibody titers following intradermal injections, it appeared that monomeric HDI was more potent to induce specific IgG(1) antibodies than the homopolymers of HDI. In summary, with respect to induction of allergy and asthma, the data presented here suggest that the homopolymeric forms of HDI appear to be less potent asthmagens, if any, than monomeric HDI.

Air Pollutants↗