Neoplasms in Rats Ingesting Acrylonitrile for Two Years

Acrylonitrile induction of rodent neoplasia: Potential mechanism of action and relevance to humans

Acrylonitrile, an industrial chemical, is a multisite carcinogen in rats and mice, producing tumors in four tissues with barrier function, that is, brain, forestomach, Zymbal’s gland, and Harderian gland. To assess mechanism(s) of action (MoA) for induction of neoplasia and to evaluate whether the findings in rodents are indicative of human hazard, data on the potential key effects produced by acrylonitrile in the four rodent target tissues of carcinogenicity were evaluated. A notable finding was depletion of glutathione in various organs, including two target tissues, the brain, and forestomach, suggesting that this effect could be a critical initiating event. An additional combination of oxidative DNA damage and cytotoxic effects of acrylonitrile and its metabolites, cyanide, and 2-cyanoethylene oxide, could initiate pro-inflammatory signaling and sustained cell and tissue injury, leading to compensatory cell proliferation and neoplastic development. The in vivo DNA-binding and genotoxicity of acrylonitrile has been studied in several target tissues with no compelling positive results. Thus, while some mutagenic effects were reported in acrylonitrile-exposed rodents, data to determine whether this mutagenicity stems from direct DNA reactivity of acrylonitrile are insufficient. Accordingly, the induction of tumors in rodents is consistent primarily with a non-genotoxic MoA, although a contribution from weak mutagenicity cannot be ruled out. Mechanistic data to support conclusions regarding human hazard from acrylonitrile exposure is weak. Comparison of metabolism of acrylonitrile between rodents and humans provide little support for human hazard. Three of the tissues affected in bioassays (forestomach, Zymbal’s gland, and Harderian gland) are present only in rodents, while the brain is anatomically different between rodents and humans, diminishing relevance of tumor induction in these tissues to human hazard. Extensive epidemiological data has not revealed causation of human cancer by acrylonitrile.

Neurobehavioral alterations in rats exposed to acrylonitrile in drinking water

This study was carried out on rodents, to explore the neurobehavioral effects of acrylonitrile (AN) administered in drinking water. Thirty, male, Sprague-Dawley rats were randomly divided into three groups: two exposure groups (50 and 200 ppm AN), and one control group (tap water without AN). Three tests, including the open field test, rotarod test and spatial water maze, were applied to evaluate locomotor activities, motor co-ordination and learning and memory, respectively, prior to initiation of the treatment, and at Week 4, 8 and 12 postexposure. There were no consistent changes in the open field test, except for locomotion and grooming episodes. In the rotarod test, AN significantly decreased the latencies to fall in a dose and time-dependent manner. In the spatial water maze test, rats exposed to AN for 12 weeks had significantly more training times and longer escape latencies than control animals. These findings indicate that oral exposure to AN induces neurobehavioral alterations in rats.

Facing the key workplace challenge: assessing and preventing exposure to nanoparticles at source

Nanomaterials present new challenges to understanding, predicting, and managing potential health risks in occupational environments. In this study, we characterize the key physical processes related to formation and growth of nanoparticles. The main focus is on various occupational environments, as these are known to be major environments with nanoparticles in indoor air. The protection of people potentially to be exposed to nanoparticles is one of the key issues in terms of risk assessment and prevention. Two of the main protection techniques that are discussed and characterized are ventilation and filtration, which are widely used in practical applications.

Cancer dose–response assessment for acrylonitrile based upon rodent brain tumor incidence: Use of epidemiologic, mechanistic, and pharmacokinetic support for nonlinearity

A cancer dose-response assessment was conducted for acrylonitrile (AN) using updated information on mechanism of action, epidemiology, toxicity, and pharmacokinetics. Although more than 10 chronic bioassays indicate that AN produces multiple tumors in rats and mice, a number of large, well-conducted epidemiology studies provide no evidence of a causal association between AN exposure and cancer mortality of any type. The epidemiological data include early industry exposures that are far higher than occur today and that approach or exceed levels found to be tumorigenic in animals. Despite the absence of positive findings in the epidemiology data, a dose-response assessment was conducted for AN based on brain tumors in rats. Mechanistic studies implicate the involvement of oxidative stress in rat brain due to a metabolite (2-cyanoethylene oxide or CEO, cyanide), but do not conclusively rule out a potential role for the direct genotoxicity of CEO. A PBPK model was used to predict internal doses (peak CEO in brain) for 12 data sets, which were pooled together to provide a consistent characterization of the dose-response relationship for brain tumor incidence in the rat. The internal dose corresponding to a 5% increase in extra risk (ED 05=0.017 mg/L brain) and its lower confidence limit (LED 05=0.014 mg/L brain) was used as the point of departure. The weight-of-evidence supports the use of a nonlinear extrapolation for the cancer dose-response assessment. A quantitative comparison of the epidemiology exposure-response data (lung and brain cancer mortality) to the rat brain tumor data in terms of internal dose adds to the confidence in the nonlinear extrapolation. Uncertainty factors of 200 and 220 (for the oral and inhalation routes, respectively) were applied to the LED 05 to account for interspecies variation, intraspecies variation, and the severity of the response measure. Accordingly, oral doses below 0.009 mg/kg-day and air concentrations below 0.1mg/m(3) are not expected to pose an appreciable risk to human populations exposed to AN.

Chronic toxicity and oncogenic dose-response effects of lifetime oral acrylonitrile exposure to Fischer 344 rats

Acrylonitrile (AN) was administered in the drinking water for approximately 2 years to groups of 100 male and 100 female Fischer 344 rats at nominal concentrations of 1, 3, 10, 30, and 100 ppm. Two groups, each of 100 males and 100 females, were used as untreated controls. Average daily intake was 0.1, 0.3, 0.8, 2.5 or 8.4 mg AN per kg body weight per day, respectively, for treated male rats and 0.1, 0.4, 1.3, 3.7, or 10.9 mg AN per kg per body weight per day, respectively, for dosed females. Clinical biochemistry, interim necropsies, organ weights and microscopic evaluation of tissues and organs were performed on groups of ten rats per sex per group at months 6, 12, and 18 and at study termination. Females were sacrificed in the 24th month and males were terminated after 26 months of dosing. A consistent decrease in survival, lower body weight and reduced water intake, as well as small reductions in hematological parameters, were observed in both sexes of the 100 ppm group. Elevated numbers of early deaths were observed in groups of males receiving 10 ppm AN and females receiving 30 ppm AN. Organ:body weight ratios at various study intervals were consistently elevated in the high dose group and likely were related to lower body weights. At these same intervals, mean absolute weights were either comparable to controls or only slightly elevated and few changes in weight ratios were seen when organ weights were compared with brain weights. No biochemical changes suggested a treatment-related effect. An increase in urine specific gravity in 100 ppm male rats was reflective of a decrease in liquid intake at this level. The only significant non-neoplastic finding observed histologically was a dose-related increase in hyperplasia/hyperkeratosis in squamous cells of the forestomach in male and female rats given 3 ppm and higher AN. This observation correlated with the induction of treatment-related squamous cell tumors (papillomas and carcinomas) of the forestomach seen primarily in rats at 3 ppm AN and higher. Mammary gland carcinomas were observed only in female groups. Both sexes given 10 ppm AN or more in their drinking water for their lifetime had astrocytomas of the brain/spinal cord and adenomas/carcinomas of the Zymbal's gland.

Two-year toxicity and oncogenicity study with acrylonitrile incorporated in the drinking water of rats

Sprague-Dawley rats (80 per sex per control and 48 per sex in each treatment group) were given drinking water formulated to contain 0, 35, 100, or 300 ppm acrylonitrile (AN) for up to 2-years. An additional ten rats per sex per group were added for a 1-year interim necropsy. The equivalent doses of AN consumed were 0, 3.4, 8.5, and 21.3 mg/kg per day for males and 0, 4.4, 10.8, and 25.0 for females. Rats were closely monitored clinically with body weight, feed and water consumption measured at numerous intervals. Hematology, clinical chemistry, and urinalysis were evaluated six times. All rats were necropsied when moribund, found dead, or at scheduled termination, with extensive histopathology of all rats. Numerous adverse toxic and oncogenic effects were observed in both sexes of all AN treatment groups. Decreased water consumption, feed consumption, and concomitant body weight suppression occurred within days of study initiation and persisted throughout the study in all treatment groups. An early onset of Zymbal gland tumors in high dose male and female rats, and in the mammary gland of all treated groups of females, was detected in-life. Hematology, clinical chemistry, and urinalysis, repeatedly evaluated, were without significant biological effects, except for an increased urine specific gravity due to the rats lower water intake. Organ weights at study termination were not significantly affected. Mortality was high in all female treated groups, with no surviving male or female 300 ppm rats during the last 2 months of the study. The most significant findings in this study were detected following gross and microscopic examination of an extensive list of tissues from all rats in the study. Nontumorous and tumorous lesions were found at an increased and/or decreased rate in a number of tissues of both sexes at all treatment levels. The primary nontumorous histopathologic effects of AN exposure occurred in the forestomach and the central nervous system of rats of both sexes and involved all treatment groups. A statistically significant increased incidence of tumors in one or more dose levels of either sex occurred in the central nervous system, Zymbal gland, forestomach, tongue, small instestine, and mammary gland. A no-observed-effect level (NOEL) was not identified in this study for toxicity or oncogenicity in either sex.

Comparative chronic toxicity and carcinogenicity of acrylonitrile by drinking water and oral intubation to Spartan Sprague-Dawley rats

Groups of 100 male and 100 female Spartan Sprague-Dawley rats were administered lifetime oral doses of Acrylonitrile (AN) by one of two routes of dosing, either at 0.1 or 10 mg/kg per day, 7 day per week by intubation or continually at 1 or 100 ppm AN in their drinking water. The doses selected were designed to approximate the same daily intake of AN in each of two separate studies, whether by a single bolus dose (intubation) or a more continuous dosing regimen in drinking water. Each study had its own untreated control group of 100 rats per sex. In the drinking water study, the equivalent mean dosage of AN administered to males and females were 0, 0.09, and 0.15 mg/kg per day, respectively, at the 1 ppm level, and 0, 8.0 and 10.7 mg/kg per day, respectively, for 100 ppm dose groups. In both studies, groups of ten rats per sex were sacrificed at 6, 12 and 18 months and at study term. Ophthalmoscopic, hematological, clinical biochemistry, urinalysis and full histopathological exams were performed on control and high dose groups of rats in each study. Similar tests were done in lower dose groups, as required, to define dose-responses of observed effects. All animals were necropsied and underwent microscopic examination of target tissues, including brain, ear canal, stomach, spinal cord and any observable tissue masses. High dose male and female rats in both studies exhibited statistically decreased body weights. Food consumption and water intake were reduced only in the drinking water study. Due to increased deaths in groups of high dose rats of both studies receiving AN, all intubation test groups were terminated after 20 months of treatment. Surviving males and females in the drinking water study were terminated after 22 and 19 months, respectively. Small, sometimes statistically significant, reductions in hemoglobin, hematocrit and erythrocyte count were observed in male and female rats in both high dose (10 mg/kg per day intubation and 100 ppm drinking water) groups from both studies. There were increases in absolute or relative organ weight ratios for liver and adrenal in the high dose intubation study groups, but could not be correlated with AN toxicity in the absence of adverse clinical biochemistry or microscopic findings. Similar organ weight findings were not observed in the drinking water study. Again, there were no changes in clinical biochemistry or microscopic findings in these tissues. Absolute kidney weights were increased in high dose male and female rats in the intubation study and high dose female rats only in the drinking water study. Male and female rats from high dose groups in each study had a higher incidence of palpable masses of the head and the nonglandular stomach and, in females only, the mammary region. In both sexes, treatment-related tumors of the central nervous system (brain, spinal cord), ear canal, and gastrointestinal tract, and in females only, the mammary gland (intubation only) were observed in rats administered either 10 mg/kg per day by intubation or 100 ppm in drinking water. Animals from the intubation study had a substantially higher incidence of AN-related site-specific tumors than did their drinking water study counterparts. While a similar spectrum of tumors was produced by both oral dosing regimens, there were some notable differences in organ-specific incidence of tumors. Astrocytomas of the brain and spinal cord were found at a higher incidence in those rats exposed continuously to AN administered in the drinking water versus bolus dosing by intubation. Conversely, a higher incidence of squamous cell carcinomas/papillomas of the forestomach and adenocarcinomas of the intestine and, in females only, carcinomas of the mammary gland were observed in high dose rats receiving AN by intubation. An increase in the degree of severity of forestomach hyperplasia was observed in all high dose groups of animals, irrespective of mode of administration. These effects were more pronounced, were correlated with a much higher incidence of forestomach tumors, and were identified earlier (12 months) in the intubation study in which there was direct tissue contact with a more concentrated AN solution. Elevations in epidermal cysts in high dose males and females in the intubation study and renal hyperplasia in high dose animals of both sexes in both studies may have a treatment relationship. All other clinical and microscopic findings were considered unremarkable. There were no discernable non-neoplastic effects attributable to treatment in groups of low dose male and female rats given AN by intubation at 0.1 mg/kg per day or 1 ppm in drinking water. The results of this study indicate a consistent spectrum of neoplastic and non-neoplastic effects produced by AN in the same rat strain, whether administered orally by bolus or by continuous dosing in the drinking water. While the spectrum of tumors and target organ toxicity produced was similar, bolus dosing clearly increased tumors associated with the gastrointestinal tract. Neoplasms found in several other tissues were most prominently displayed in groups of more continuously dosed rats.

Mutagenicity, carcinogenicity, and teratogenicity of acrylonitrile

Acrylonitrile (AN) is an important intermediary for the synthesis of a variety of organic products, such as artificial fibres, household articles and resins. Although acute effects are the primary concern for an exposure to AN, potential genotoxic, carcinogenic and teratogenic risks of AN have to be taken seriously in view of the large number of workers employed in such industries and the world-wide population using products containing and possibly liberating AN. An understanding of the effect of acrylonitrile must be based on a characterization of its metabolism as well as of the resulting products and their genotoxic properties. Tests for mutagenicity in bacteria have in general been positive, those in plants and on unscheduled DNA synthesis doubtful, and those on chromosome aberrations in vivo negative. Wherever positive results had been obtained, metabolic activation of AN appeared to be a prerequisite. The extent to which such mutagenic effects are significant in man depends, however, also on the conditions of exposure. It appears from the limited data that the ultimate mutagenic factor(s), such as 2-cyanoethylene oxide, may have little opportunity to act under conditions where people are exposed because it is formed only in small amounts and is rapidly degraded. The carcinogenic action of AN has been evaluated by various agencies and ranged from 'reasonably be anticipated to be a human carcinogen' to 'cannot be excluded', the most recent evaluation being 'possibly carcinogenic to humans'. Animal data that confirm the carcinogenic potential of AN have certain limitations with respect to the choice of species, type of tumors and length of follow up. Epidemiological studies which sometimes, but not always, yielded positive results, encounter the usual difficulties of confounding factors in chemical industries. Exposure of workers to AN should continue to be carefully monitored, but AN would not have to be considered a cancer risk to the population provided limitations on releases from consumer products and guidelines on AN in water and air are enforced. AN is teratogenic in laboratory animals (rat, hamster) at high doses when foetal/embryonic (and maternal) toxicity already is manifest. Pregnant workers should not be exposed to AN. In view of the small concentrations generally encountered outside plants, women not professionally exposed would appear not to be at risk of teratogenic effects due to AN. Future research should concentrate on the elucidation of the different degradation pathways in man and on epidemiological studies in workers including pregnant women, assessing also, if possible, individual exposure by bio-monitoring.

Evaluation of possible genotoxic mechanisms for acrylonitrile tumorigenicity

Acrylonitrile (ACN) exposure is associated with tumors in rat brain, Zymbal gland, and mammary gland. Adducts affecting base pairing were formed in isolated DNA exposed in vitro to the ACN metabolite cyanoethylene oxide (CNEO). DNA from liver, which is not a cancer target organ in ACN-exposed rats, contained low levels of 7-(2-oxoethyl)guanine, and adduct believed not to interfere with base pairing. No adducts have been detected in brain DNA from ACN-exposed rats, suggesting that brain tumors may have arisen by mechanisms other than ACN-DNA reactivity. Genotoxicity assays of ACN have indicated no particular carcinogenic mechanism. Positive reverse mutagenesis in Salmonella typhimurium HisG46 base substitution tester strains by ACN is attributable to CNEO. Other in vitro genotoxicity test assays of ACN have yielded mixed results, without consistent effect of metabolic activation. Some positive genotoxicity data for ACN appear to result from artifacts or from non-DNA-reactive mechanisms. In vivo micronucleus, chromosome aberration, and autoradiographic unscheduled DNA synthesis assays were negative for ACN. The comparative genotoxicity of vinyl chloride and ACN indicates that despite other similarities, they cause rodent tumors by different mechanisms. Also, they absence of ACN-DNA adduct formation in the rat brain suggests the operation of epigenetic mechanisms.

Acrylonitrile: a reevaluation of the database to support an inhalation cancer risk assessment

Acrylonitrile (ACN) is a monomer used extensively in the production of plastics, synthetic fibers, and rubber. In previous assessments conducted by IARC and the EPA, ACN was classified as a probable human carcinogen based on limited evidence in humans and sufficient evidence in laboratory animals. Specifically, EPA had determined that there was an association between ACN exposure and lung cancer based on a study by O'Berg (1980, J. Occup. Med. 22, 245-252). However, a follow-up of this cohort (O'Berg et al., 1985, J. Occup. Med. 27, 835-840) shows no statistically significant excess of lung cancer mortality or incidence. Our evaluation of the more recent human database taken as a whole shows that there is not a clear association between ACN exposure and human cancer, yet the studies have insufficient power to be able to rule out a small increase. In laboratory rats, however, ACN has been shown to be clearly carcinogenic by the oral and inhalation routes. Applying the methodology of EPA's proposed 1996 cancer risk assessment guidelines to the rat tumor data, the estimated upper bound on the excess lifetime risk at continuous exposure to 1 microgram/m3 ACN is calculated to be in the range of 8.2 x 10(-6) to 1.1 x 10(-5).

Effects of drugs on pituitary fine structure in laboratory animals

Although an increasing number of chemicals are reported to affect endocrine glands, only a few studies are dealing with their toxic effect on pituitary. The drugs can induce lesions acting directly on endocrine cells or indirectly by interfering with the regulation of their endocrine activities. Some drugs stimulate pituitary cell proliferation leading to hyperplasia and tumor formation; other chemicals have an inhibitory effect on adenohypophysial cells; and only one drug, hexadimethrine bromide, has been found to induce pituitary necrosis. Although complex toxicologic studies have been carried out on many chemicals, the mechanism of action of most drugs is not completely elucidated and further studies are necessary to establish structure function correlations.