Wollastonite toxicity: an update.

This review updates earlier work addressing the epidemiology and toxicity of wollastonite. Earlier chronic animal bioassay and human mortality data were inadequate (IARC term) or negative and no new studies of these types have been published. Wollastonite has been determined to have low biopersistence in both in vivo and in vitro studies, which probably accounts for its relative lack of toxicity. Earlier morbidity studies of mining/mineral processing facilities in Finland and New York State indicated that exposure to wollastonite might result in pleural plaques (Finland) or decrements in certain measures of lung function (New York). More recent analysis of data from an ongoing health surveillance program at one facility (New York) indicates that there are no pleural plaques or interstitial lung disease or decrements in lung function among never smokers or former smokers occupationally exposed to wollastonite. This result probably reflects continued reduction in exposures as part of an ongoing product stewardship program at this facility and suggests that wollastonite has relatively low toxicity as currently managed.

Commentary: further comments on Mycoplasma pulmonis and lymphoma in bioassays of rats.

The authors recently assessed the likelihood that lifetime cancer bioassays of aspartame, methanol, and methyl tertiary butyl ether conducted with conventional (not specific pathogen free) Sprague-Dawley rats were compromised by Mycoplasma pulmonis disease. From the tumor data and other information, the authors concluded that the rats used in these bioassays likely had M pulmonis disease and that lesions of the disease were plausibly interpreted as lymphoma. Subsequently, they analyzed the nonneoplastic lesion data from these bioassays for occurrence of inflammatory lesions and found that 2,267 of 2,960 rats (76.6%) were reported to have bronchitis, the signature lesion of M pulmonis disease, and that 633 rats (21.4%) were reported to have otitis, another common lesion of the disease. Also, documentation is now available containing serologic evidence of mycoplasma infection in the rats. In contrast, the reports of 6 National Toxicology Program bioassays based on specific pathogen-free Sprague-Dawley rats listed no instances of bronchitis or otitis. These findings provide substantial additional evidence that the bioassays in question were compromised by M pulmonis disease. Therefore, the reported induction of lymphoma in these studies should not be considered in cancer risk assessments. The authors also found that inflammatory lesions were prevalent in lymph nodes, thymus, pleura, and brain. Finally, they found that of all 328 cases of lymphoimmunoblastic lymphoma affecting the lung (the primary form of lymphoma reported), 218 (66.5%) occurred within the first 104 weeks of the studies, showing that occurrence of such lesions was not due to appearance in rats surviving beyond that interval.

Induction of tunica vaginalis mesotheliomas in rats by xenobiotics.

To better understand the relevance of tunica vaginalis mesotheliomas (TVM) to human cancer risk, we examined the nature of TVM responses in 21 published rat cancer bioassays against the backdrop of the biology and molecular biology of mesothelium, and of spontaneous and treatment-induced TVM. Although relatively rare in all species including humans, TVM are seen most frequently in F344 male rats, as opposed to other rat strains, and are causally associated with the high background incidence of Leydig-cell tumors of the testes of these rats. Hormone imbalance brought about by perturbations of the endocrine system is proposed as a key factor leading to both spontaneous and treatment-associated TVM. Of 21 F344 rat studies with a treatment-associated TVM response, 7 were judged to have a nonsignificant to marginal response, 11 had a robust TVM response, and 3 were noninformative due to early mortality from other induced tumors. Of the 11 chemicals with robust responses, 8 were directly mutagenic in Salmonella and 3 are known to be mutagenic after metabolism. Only 2 of the 7 with nonsignificant to marginal responses were Ames test positive. TVM induction is a male F344 rat-specific event, and chemicals/agents that induce only TVM in the male F344 rat from a typical two-sex rat and mouse chronic bioassay are likely irrelevant in human risk assessment.

Dioxin in soil: bioavailability after ingestion by rats and guinea pigs.

Soil environmentally contaminated with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) was given by gavage to guinea pigs and rats. The development of a characteristic clinicopathologic syndrome in guinea pigs, the induction of aryl hydrocarbon hydroxylase in rats, and the presence of TCDD in the livers of both species show that TCDD in soil exhibits high biological availability after ingestion.

Mycoplasma pulmonis and lymphoma in bioassays in rats.

Lymphomas were reported to be induced in rats in bioassays of aspartame, methyl-tertiary-butyl ether (MTBE), and other chemicals conducted by a nonprofit cancer research organization. European regulatory authorities concluded that lymphomas in the aspartame study were caused by Mycoplasma pulmonis and suggested that this also was the case for the MTBE bioassay. To assess the role of M. pulmonis in these bioassays, we reviewed the tumor data for the aspartame and MTBE bioassays and, additionally, the organization's bioassay of methanol. For all 3 studies, the most frequently reported hematopoietic neoplasm was lympho-immunoblastic lymphoma, the most frequently affected organ was the lung, and, in almost half of the rats with this diagnosis, the lung was the only affected organ. Lesions diagnosed as lymphoma in published illustrations had pleomorphic cellular morphology and appeared to contain neutrophils. Information from these reports and other sources indicated that lesions typical of M. pulmonis disease were prevalent among the aspartame and MTBE study rats and that the rats were not specific-pathogen-free. Because the lymphoma type, cellular morphology, and organ distribution reported in these studies are atypical of lymphoma in rats, because lymphocyte and plasma cell accumulation in the lung is characteristic of M. pulmonis disease, and because M. pulmonis disease can be exacerbated by experimental manipulations, including chemical treatment, we suggest that a plausible alternative explanation for the reported results of these bioassays is that the studies were confounded by M. pulmonis disease and that lesions of the disease were interpreted as lymphoma.

Product stewardship in wollastonite production.

In July 2002, NYCO Minerals, Inc., discovered a heretofore unknown contaminant in its wollastonite ore. The contaminant was first believed to be tremolite asbestos. Immediate efforts were made to eliminate this material. Additional studies were initiated to fully characterize the contaminant and its distribution in the ore body. Subsequent study by NYCO and their consultants led to the identification of the contaminant as a transition material (TM) intermediate between tremolite and talc. In vitro dissolution rate measurements indicated that the TM dissolved much more rapidly than tremolite asbestos. This article provides background information on wollastonite mineralogy and NYCO's product stewardship program (PSP). At present, NYCO Minerals uses selective mining to control the trace levels of TM in the ore and finished product verified by periodic monitoring of workplace air and finished product.

Natural history of body weight gain, survival, and neoplasia in the F344 rat.

This study involved the fact that knowledge of the natural incidence of neoplastic lesions is essential for interpretation of experiments designed to reveal the effects of potential carcinogens. Although the F344 rat is widely used in chronic (2-yr) testing programs, the natural history of neoplasia after 24 months is not known; thus this study, with 529 male and 529 female inbred F344 rats, was designed to deal with this aspect. This report also included information on growth and longevity. In addition, the tumor rates found in this study were compared with 2-year historic control tumor rates; results revealed the following. 1) Maximum mean body weights were 468 and 330 g for males and females, respectively. Peak weight in males was reached at 77 weeks of age and in females, at 107 weeks of age. 2) There was no clear sex difference in longevity; a median life-span (50% survival age) or 28 months was recorded in both sexes. 3) Variety of neoplastic lesions in animals that were allowed to live out their life-span was not greater than that in animals that were killed between 110 and 116 weeks of age; thus older age was not characterized by unique neoplasms. 4) The incidence of certain neoplasms increased markedly after 110-116 weeks. The data indicated that life-span studies in F344 rats had no advantages over 2-year studies. However, availability of life-span data is essential for interpretation of the 2-year studies.

Guidelines for combining neoplasms for evaluation of rodent carcinogenesis studies.

In a continuing review of long-term toxicology and carcinogenesis studies in rats and mice, the National Toxicology Program (NTP) is confronted with many problems concerning the interpretation of tumor data. A frequently raised question is: "Should certain neoplasms be combined for overall assessment of rodent carcinogenesis data?" NTP policy is that certain neoplasms may be combined for statistical assessment of tumor data and that hyperplastic responses may be used as supportive evidence. The primary reason for combining neoplastic lesions is to gain more insight into the evidence of the carcinogenicity of a given chemical in that species of animal. This report gives the rationale, criteria, and guidelines used by the NTP for combining neoplasms for the evaluation of long-term rodent toxicology and carcinogenesis studies. The guidelines are based mainly on lesions occurring in the F344/N inbred rat and (C57BL/6 X C3H)F1 mouse and may or may not be appropriate for other strains or species. The concepts of combining neoplasms and sites should be viewed in terms of the study as a whole, since tumor formation is only one of many responses caused by chemicals in mammals. The resulting information becomes part of the "weight of the evidence" for estimating the potential hazard of a given chemical.

Neoplasms observed in untreated and corn oil gavage control groups of F344/N rats and (C57BL/6N X C3H/HeN)F1 (B6C3F1) mice.

Control data on F344/N rats and (C57BL/6N X C3H/HeN)F1 (B6C3F1) mammary tumor virus-free mice from the National Toxicology Program (NTP) were examined to determine if animals receiving corn oil by gavage showed tumor incidences that differed from those of untreated control animals. Analyses of these data were adjusted for interlaboratory variability, time-related trends, and supplier effects. Two biologically significant effects were found: Male F344/N control rats receiving corn oil by gavage showed a higher (P less than .05) incidence of pancreatic acinar cell adenoma and a lower (P less than .001) incidence of leukemia (primarily mononuclear cell leukemia) than did the corresponding untreated controls. The increased incidences of pancreatic acinar cell adenoma seen in male rats administered corn oil by gavage were associated with elevated body weights observed in these animals relative to untreated controls. Female F344 rats and male and female B6C3F1 mice showed little or no evidence of a difference in tumor incidence between corn oil gavage-treated and untreated controls. A review of nearly 300 carcinogenesis studies done by the National Cancer Institute (NCI) and the NTP revealed that there were no corn oil gavage studies in which increased incidences of pancreatic acinar cell tumors or leukemia in male F344/N rats were the sole evidence of the carcinogenicity of a test chemical. Thus use of corn oil appears to have little impact on the interpretation of NCI-NTP carcinogenicity studies.

Induction of colon tumors by a single oral dose of 1,2-dimethylhydrazine.

Male Fischer rats were treated at 7 weeks of age with a single oral dose of 1,2-dimethylhydrazine (35 mg/kg). After 1.5 years, the 14 control and 28 treated animals were killed for general autopsy. The incidence of tumor formation in the treated animals was 78.6% as compared to 0% for the control animals. All tumors (1--3/rat) were located in the colon, with the exception of one in the Zymbal's gland of the ear and one in the small intestine. The dosage of 1,2-dimethylhydrazine used in this study is the lowest single oral dose of this carcinogen reported to induce colon tumors.

Dose response of 1,2-dimethylhydrazine and methylazoxymethanol acetate in the F 344 rat.

Weanling male and female F 344 rats were given various doses of 1,2-dimethylhydrazine (DMH) or methylazoxymethyl acetate (MAMAc), and were then held for 46-64 weeks in an effort to determine a dose response and establish a dose level which would produce a low level of intestinal neoplasia with a minimal number of tumors in other organs. DMH proved superior to MAM in this respect, although liver lesions were still observed with both compounds at the lowest carcinogenic intestinal dose.

Comparative toxicity of PCBs and related compounds in various species of animals.

There are several basic principles that apply to the clinicopathologic syndrome produced by polychlorinated biphenyls (PCBs). They are as follows: The degree of halogenation and position of the halogen atoms determine the potency of PCB, PBB, CDD, CDF and CN; in a given species of animals, the clinicopathologic syndrome induced by PCB is comparable to that induced by polybrominated biphenyls (PBB), chlorinated dibenzo-p-dioxins (CDD), chlorinated dibenzofurans (CDF), and chlorinated naphthalenes (CN) when an equitoxic dose is achieved; The clinicopathologic syndrome is different in each species of animals; Different species of animals vary in their susceptibility to intoxication; intoxication is more readily effected in young animals that in adults; at lethal doses the time between exposure and death is prolonged (greater than 2 weeks).

Comparative results of 327 chemical carcinogenicity studies.

The National Cancer Institute (NCI) and the National Toxicology Program (NTP) have carried out a number of laboratory animal carcinogenicity studies and presented the results of these experiments in a series of Technical Reports. This paper tabulates the results of the 327 NCI/NTP studies carried out to date on 308 distinct chemicals, and discusses certain issues relevant to the evaluation of carcinogenicity in these experiments. This compilation of results from NCI/NTP carcinogenicity experiments provides a large database that can be used to study structure-activity correlations, interspecies concordance, and associations between laboratory animal carcinogenicity and other toxicological effects.

Structure-induction versus structure-toxicity relationships for polychlorinated biphenyls and related aromatic hydrocarbons.

A comparison of the structure-induction (involving rat and mouse Ah receptor binding) and structure-toxicity (in vivo guinea pig toxicity) relationships suggests that two receptors with structurally distinct binding properties may be involved. This is supported by demonstration of potentiated toxicity through a mechanism believed to involve the Ah receptor as a site of loss with respect to toxicity. Theoretical and working models are proposed for these separate receptors to aid in the search for other relevant binding proteins. The findings suggest that polychlorinated biphenyls that are relatively low in toxicity may have modulating properties on the action of highly toxic compounds with which they are normally found in the environment.

Chronic effects of dietary exposure to amosite and chrysotile asbestos in Syrian golden hamsters.

Bioassays of amosite, short-range (SR), intermediate-range (IR) or intermediate-range chrysotile asbestos in combination with the intestinal carcinogen 1,2-dimethylhydrazine dihydrochloride (DMH) were conducted with male and female Syrian golden hamsters. Amosite and both forms of chrysotile asbestos were administered at a concentration of 1% in pelleted diet for the entire lifetime of the hamsters starting with mothers of the test animals. Group sizes varied from 125-254. There was no adverse effect on body weight gain or survival by either type of asbestos or by IR chrysotile asbestos in combination with DMH. A significant increase (p less than 0.05) in adrenal cortical tumors was observed in male hamsters exposed to SR and IR chrysotile asbestos and in females treated with IR chrysotile asbestos when compared to the pooled control groups. However, statistical significance (p less than 0.05) was lost when these dosed groups were compared with temporal control groups. Neither of the male or female amosite asbestos groups showed increased neoplasia in any tissue or organ compared to the control groups. The cocarcinogen studies using IR chrysotile asbestos and 1,2-dimethylhydrazine dihydrochloride were considered inadequate because there was no increase in intestinal neoplasia in the DMH group.

Chronic effects of dietary exposure to amosite asbestos and tremolite in F344 rats.

Carcinogenesis bioassays of blocky (nonfibrous) tremolite and amosite asbestos alone or in combination with the intestinal carcinogen 1,2-dimethylhydrazine dihydrochloride (DMH) were conducted with male and female Fischer 344 rats. The minerals were administered at a concentration of 1% in pelleted diet for the entire lifetime of the rats starting with the dams of the test animals. One group of amosite rats also received chrysotile asbestos via gavage during lactation. Group sizes varied from 100 to 250 animals. The offspring from mothers exposed to tremolite or amosite asbestos were smaller at weaning than those from untreated mothers and remained smaller throughout their life. The administration of dimethylhydrazine (DMH) did not affect body weight gain, either in amosite-exposed or nonexposed animals. Survival was comparable in the tremolite and control groups. The amosite-exposed rats showed enhanced survival compared to the untreated controls. DMH exposure reduced survival by approximately one year, although the amosite plus DMH groups survived slightly better than the DMH alone groups. No toxicity or increase in neoplasia was observed in the tremolite-exposed rats compared to the controls. Significant increases (p less than 0.05) in the rates of C-cell carcinomas of the thyroid and monocytic (mononuclear cell) leukemia in male rats were observed in amosite-exposed groups. However, the biological significance of the C-cell carcinomas in relation to amosite asbestos exposure is discounted because of a lack of significance when C-cell adenomas and carcinomas were combined and the positive effect was not observed in the amosite plus preweaning gavage group. The biological significance of an increased incidence of mononuclear cell leukemia is questionable, because of a lack of statistical significance in the amosite group when evaluated using life table analysis, lack of significance when compared to the tremolite control group, and the fact that no toxic or neoplastic lesions were observed in the target organs, i.e., gastrointestinal tract and mesothelium. DMH caused a high rate of (62-74%) of intestinal neoplasia in amosite and nonamosite-exposed groups. Neither an enhanced carcinogenic nor protective effect was demonstrated by exposure to amosite asbestos.

Relationship between lung biopersistence and biological effects of man-made vitreous fibers after chronic inhalation in rats.

This article describes the relationship between fiber biopersistence and the chronic toxicity of different chemical compositions of man-made vitreous fibers (MMVF) in the lung. Rats were exposed in "nose-only" inhalation chambers, 6 hr/day, 5 days/week, for 24 months to aerosol concentrations of 30 mg/m3 containing comparable fiber numbers and similar dimensions of fibrous glass (FG) or refractory ceramic fiber (RCF). Interim sacrifices were performed periodically to monitor fiber number and dimensions in the lung and the progression of pulmonary alterations. At each interim sacrifice, three to six recovery animals were removed from each exposure group and held until two years to determine the biopersistence of fibers after different exposure times. Fibers were recovered from the ashed lungs, counted, and measured using optical and scanning electron microscopy (SEM). Fiber chemistry was assessed in 91-week recovery lungs using energy dispersive spectroscopy (EDS) analysis. RCF induced lung fibrosis and an elevation in lung tumors and pleural mesotheliomas. FG exposure resulted in no lung fibrosis, no statistically significant increase in the lung tumor incidence, and no mesotheliomas. After two years of continuous exposure, the number of World Health Organization fibers per milligram dry lung recovered from RCF and FG exposed lungs was comparable. EDS analysis of recovery lungs showed that most of the alkalis and alkaline earths had leached from the FG fibers over time. A slight change in RCF chemistry was observed. These findings indicate that the change in the chemical composition of fibers may be an important determinant of the chronic toxicity of MMVFs.

Carcinogenicity testing of phthalate esters and related compounds by the National Toxicology Program and the National Cancer Institute.

Five phthalate ester and related compounds (phthalic anhydride, phthalamide, di(2-ethylhexyl) phthalate, di(2-ethylhexyl) adipate and butyl benzyl phthalate) have been tested for carcinogenic effects in standard lifetime rodent feeding studies. Groups of 50 male and female rats and mice were fed diets containing various concentrations of the test chemicals for 102-106 consecutive weeks. The dietary concentrations were estimated to be maximally tolerated doses and half maximally tolerated doses. All animals that died during the study and all survivors at the end of two years were examined grossly and microscopically for the presence of tumors. The incidences of animals with tumors at a specific anatomic site in the treated groups and the controls were compared statistically. Neither phthalamide nor phthalic anhydride increased tumor incidences in rats or mice. Di(2-ethylhexyl) phthalate increased the incidences of liver tumors in rats and mice of both sexes, while di(2-ethylhexyl) adipate caused liver tumors in male and female mice, only. Butyl benzyl phthalate did not cause tumors in male or female mice, but the incidence of myelomonocytic leukemia in butyl benzyl phthalate-treated female rats was significantly greater than that in the controls. Chemically induced early deaths in the butyl benzyl phthalate-treated male rats precluded an evaluation of carcinogenic potential in this sex. Under the conditions of these tests, di(2-ethylhexyl) adipate was considered to be carcinogenic in both rats and mice and di(2-ethylhexyl) adipate was considered to be carcinogenic in mice. The evidence for carcinogenic effects of butyl benzyl phthalate in female rats was judged to be equivocal because of the variable nature of the incidence of myelomonocytic leukemia in Fischer 344 rats. Phthalamide and phthalic anhydride did not exhibit carcinogenic effects in these studies.

Chronic inhalation and biopersistence of refractory ceramic fiber in rats and hamsters.

Lifetime "nose-only" inhalation studies were conducted in rats using four types of refractory ceramic fibers (FCF), 1 micron in diameter x 22 to 26 microns length: High Purity, Kaolin, Zirconia, and After-Service; and on hamsters using Kaolin RCF. For comparison, animals also were exposed to chrysotile fibers. Rats were exposed 6 hr/day, 5 days/week for 24 months to concentrations ranging between 3 and 30 mg/m3. Time- and dose-dependent lesions in the rat included the development of interstitial fibrosis, pleural fibrosis, pulmonary tumors, and mesothelioma. Exposure to 3, 9 or 16 mg/m3 produced no excess lung tumors; no fibrosis was seen at 3 mg/m3. A significant increase in lung tumors and interstitial fibrosis was observed at 30 mg/m3. A single mesothelioma was observed in rats exposed to 9 mg/m3, while two occurred at 30 mg/m3. Hamsters were similarly exposed to 30 mg/m3 Kaolin RCF for 18 months; no lung tumors were induced, but pulmonary and pleural fibrosis were observed and there was a 42% incidence of mesothelioma. Multiple interim sacrifices together with recovery animals allowed detailed assessment of the lung burden of RCF, which was found to be dose related and, at the high doses, exceeded 10(5) fibers/mg of dry lung. During the various recovery periods there was a clear reduction in fiber burden. Mathematical modeling of these data for deposition, clearance, and retention and for species is currently underway.