Abstract  Induction of cytochrome P450 (CYP1A), as measured by liver ethoxyresorufin-O-deethylase (EROD) activity in juvenile rainbow trout (Oncorhynchus mykiss), was used to derive relative potency factors (RPFs) for several polycyclic aromatic hydrocarbons (PAHs), chosen for their induction potency in a rainbow trout liver cell line (RTL-W1). Potency for causing induction was estimated as the median effective concentration (EC50) from exposure-response curves. With the exception of phenanthrene, all PAHs tested induced EROD activity in juvenile trout, ranked as: benzo[k]fluoranthene>benzo[b]fluoranthene>benzo[b]fluorene>beta-napthoflavone>retene (7-isopropyl-1-methylphenanthrene). When induction potency was expressed relative to benzo[k]fluoranthene, RPFs ranged from 0.02 to 1, and the rank order in vivo was identical to the rank order with RTL-W1-derived values. The additivity of PAHs in mixtures in RTL-W1 cells was compared to whole-fish results from a previous study. EROD induction showed additive interactions for PAHs with exposure-response curves of similar slopes. This study demonstrates that assays of CYP1A induction using rainbow trout liver cells in culture would be a convenient substitute for assays with whole fish as part of testing programs for risk assessment of PAHs.

Abstract  The hydrodehalogenation of polychlorinated phenyls and biphenyls (PCBs), catalysed by palladium N-heterocyclic carbene complexes, proceeds with excellent yields, at very low catalyst loadings and at room temperature, using isopropanol as the hydrogen source and NaOH as the base.

Abstract  Illegal dumping of polychlorinated biphenyl (PCB) capacitors was discovered in Kobe, Japan, in 2001, leaving about 68 m(3) (92 tons) of soil contaminated with approximately 6.6 kg of PCBs. Solvent extraction technology carried out in 2002-2003 using isopropyl alcohol remedied the affected soil at the site. Forty-seven batch treatments were conducted during full-scale treatment. On average, 8.4 extraction cycles per batch were needed to achieve the clean-up goal for PCBs (i.e., the Japanese environmental quality standard for soil). Analytical results showed that the average PCB concentration (88 microg g(-1)-dry soil) in untreated soil samples of all the batches was decreased to 1.2 microg g(-1)-dry soil in treated soil samples, yielding a removal efficiency of 98.6%. Dioxin responsive-chemical activated luciferase gene expression assay (DR-CALUX) and enzyme-linked immunosorbent assay (ELISA) adopting a monoclonal antibody against 2,3',4,4',5-pentachlorobiphenyl (PCB #118) were used to rapidly screen soil samples before and after solvent extraction. The DR-CALUX and ELISA results were in good agreement with World Health Organization toxicity equivalent values and analytically determined PCB concentrations, respectively. Regular monitoring during the treatment period confirmed that the applied technology met Japanese environmental and control regulations concerning treatment and disposal of contaminated soils and treatment residues. After full-scale treatment, the amount of PCBs recovered from the solvent purification system approximated the estimated amount of PCBs spilled.

Abstract  The mechanism of organic nitrate tolerance is poorly defined. We studied the rat P450-catalyzed conversion of organic nitrate to nitric oxide (NO) by purified P450 isoforms relationship between P450 expression and nitrate tolerance following continuous infusion of organic nitrates in rats. The hypotensive effect of an nitroglycerin (NTG) bolus injection was abolished in rats that had been previously provided a continuous 48 h infusion of NTG. This effect was accompanied by a gradual but marked decrease in plasma and urinary nitrate levels following a peak at 18-24 h. Nitrate tolerance was reversible; the decline in the hypotensive effect and P450 levels observed after 2 d of continuous infusion was followed by restoration to control levels 2 d after cessation of the infusion. Similarly, the hypotensive action disappeared in P450-depleted, and -inhibited rats. At 48 h after infusion, NTG-induced NO generation of the vessels increased in acetone (a P450 inducer) -pretreated rats. The appearance and disappearance of P450 paralleled the conversion of organic nitrates to NO. Our observations indicate that nitrate tolerance is in large part the result of decreased P450 expression and activity. Interventions that maintain or increase P450 activity may be a strategy to provide relief from ischemic conditions in humans.

Abstract  The potential for anaerobic biodegradation of 1,1,1-trichloro-2,2-bischlorophenylethane (DDT), 1,1-dichloro-2,2,-bischlorophenylethane (DDD), and dichlorodiphenylchloroethylene (DDE) in anoxic sediment slurries collected from the Keelung River was investigated in this study. o,p'- and p,p'-DDT were dechlorinated to o,p'- and p,p'-DDD, respectively, and then transformed to other compound(s). 1-Chloro-2,2-bis (p-chlorophenyl) ethylene (DDMU) and trace amount of dichlorobenzophenone (DBP) were detected in sediment slurries amended with p,p'-DDT or p,p'-DDD. DDMU was also detected in sediment slurries amended with p,p'-DDE. The relative transformation rates for both o,p'- and p,p'-isomers of DDT, DDD, and DDE were DDT>DDD>DDE. Re-addition of DDT, DDD, or DDE to the sediment slurries after initial removal enhanced the respective dechlorination rates. The transformation rates of the p,p'-isomers of both DDT and DDD were faster than those of the respective o,p'-isomers. p,p'-DDT dechlorination in the p,p'-DDT-adapted sediment slurries were inhibited by the addition of molybdate, or molybdate plus sulfate, but not inhibited by the addition of sulfate. Addition of bromoethane-sulfonic acid (BESA) slightly inhibited p,p'-DDT dechlorination. Non-adapted sediment slurries lost the ability to dechlorinate pentachlorophenol during adaptation to p,p'-DDT. p,p'-DDD was the major transformation product of p, p'-DDT in 3,4,4',5-tetrachlorobiphenyl-adapted sediment slurries, which suggested that the microbial community in the 3,4,4',5-CB-adapted sediment was unable to remove chlorine from the aromatic rings of p,p'-DDT.

Abstract  HEEP COPYRIGHT: BIOL ABS. Guinea pigs were fed cabbage grown on municipal sewage sludge from Syracuse, New York, USA, or soil (control) as 45% of their diet for 100 days. Among 45 elements determined, Cd, Cu, Ni, Pb and Zn were higher in the sludge grown cabbage and specific tissues of the fed animals than controls. Cd was elevated in kidney, liver and spleen, while only liver exhibited increased Pb levels in guinea pigs fed the sludge grown plants. Polychlorinated biphenyls were found at higher concentrations in the sludge-grown cabbage and livers of the fed guinea pigs than in the controls. Intestinal aryl hydrocarbon hydroxylase activity was 129% higher than controls in the animals fed the sludge grown cabbage. All animals grew normally and showed no signs of overt heavy metal toxicosis.

Abstract  HEEP COPYRIGHT: BIOL ABS. PESTICIDES HEAVY METALS CARCINOGENESIS

Abstract  HEEP COPYRIGHT: BIOL ABS. MYTILUS-EDULIS INDICATOR ORGANISM POLY CHLORINATED BI PHENYL SILVER ZINC CADMIUM TIN CHROMIUM LEAD COPPER NICKEL DIGESTIVE GLAND GONAD MUSCLE

Abstract  HEEP COPYRIGHT: BIOL ABS. Grab samples of sediment were collected at 530 locations in Lake Michigan, primarily in the SE quarter of the lake. Each sample was analyzed in the field and in the laboratory for fallout 137-Cs. Twenty-five of the samples, collected near the mouth of the St. Joseph River, were analyzed in the laboratory for 11 other man-made materials known to be discharged into the river. Two statistical methods were used to determine if 137-Cs can be used as an environmental tracer to predict the areal distributions of other man-made materials. Fallout 137-Cs is a moderate to good tracer for locating areas of accumulation of 238-Pu, 239-Pu, Zn, Cu, Cr, Pb, dieldrin, DDT and polychlorinated biphenyls in sediment. Little or no correlation is found between fallout 137-Cs and 90Sr or Ni.

Abstract  In this article, we illustrate the challenges and bottlenecks in the metabolic engineering of bacteria destined for environmental bioremediation, by reporting current efforts to construct Pseudomonas strains genetically designed for degradation of the recalcitrant compound 2-chlorotoluene. The assembled pathway includes one catabolic segment encoding the toluene dioxygenase of the TOD system of Pseudomonas putina F1 (todC1C2BA), which affords the bioconversion of 2-chlorotoluene into 2-chlorobenzaldehyde by virtue of its residual methyl-monooxygenase activity on o-substituted substrates. A second catabolic segment encoded the entire upper TOL pathway from pWW0 plasmid of P. putida mt-2. The enzymes, benzyl alcohol dehydrogenase (encoded by xylB) and benzaldehyde dehydrogenase (xylC) of this segment accept o-chloro-substituted substrates all the way down to 2-chlorobenzoate. These TOL and TOD segments were assembled in separate mini-Tn5 transposon vectors, such that expression of the encoded genes was dependent on the toluene-responsive Pu promoter of the TOL plasmid and the cognate XylR regulator. Such gene cassettes (mini-Tn5 [UPP2] and mini-Tn5 [TOD2]) were inserted in the chromosome of the 2-chlorobenzoate degraders Pseudomonas aeruginosa PA142 and P. aeruginosa JB2. GC-MS analysis of the metabolic intermediates present in the culture media of the resulting strains verified that these possessed, not only the genetic information, but also the functional ability to mineralise 2-chlorotoluene. However, although these strains did convert the substrate into 2-chlorobenzoate, they failed to grow on 2-chlorotoluene as the only carbon source. These results pinpoint the rate of the metabolic fluxes, the non-productive spill of side-metabolites and the physiological control of degradative pathways as the real bottlenecks for degradation of certain pollutants, rather than the theoretical enzymatic and genetic fitness of the recombinant bacteria to the process. Choices to address this general problem are discussed. (C) 2001 Elsevier Science B.V. All rights reserved.

Abstract  BIOSIS COPYRIGHT: BIOL ABS. Although aerobic microbial biodegradation of polychlorinated biphenyls (PCBs) has been widely demonstrated in the laboratory, there is little direct evidence that this process occurs naturally in the environment. A clear indicator of naturally occurring aerobic PCB biodegradation would be the presence of intermediate metabolites such as chlorobenzoic acids (CBAs) in contaminated sediments. CBAs have been detected in contaminated sediment cores, and their concentration profiles were correlated with PCB depth profiles. From the congener distribution pattern of the CBAs detected, it is extremely unlikely that these compounds were derived from either the breakdown of chlorinated herbicides or the carboxylation of phenols. No CBAs were detected in sediment samples not contaminated with PCBs. In addition, other metabolites which are less prone to source ambiguity, including 2,3-dihydro-2,3-dihydroxy-2'-chlorobiphenyl and 2,3-dihydroxy-2'-chlorobiphenyl, have also been detecte

Abstract  BIOSIS COPYRIGHT: BIOL ABS. RRM METAL POLLUTION

Abstract  This article is a summary of a study on the exposure to dust and harmful substances in Germany during the disassembly and shredding of discarded electrical and electronic equipment. Dust samples were taken in 16 plants at critical workplaces which had been identified in an earlier study of work procedures. Heavy-metal concentrations were determined in the dust samples. Dust samples taken in the vicinity of the shredder were also analysed for polychlorinated biphenyls, chlorinated dioxins and furans, and brominated dioxins. The concentrations of fine dust that penetrates into the alveoles were below the limit of 6mg/m³ in all plants studied. The 10mg/m³ recommended limit for total respirable dust was exceeded by 5% of the measurements. The exposure to heavy metals was low when old refrigerators or washing machines were dismantled, but it was extremely high during processing of television tubes. While the concentrations of polychlorinated biphenyls and chlorinated dioxins complied with exposure limits, those of brominated dioxins were above the limit in one third of the samples.

Abstract  The thermostable catechol 2,3-dioxygenase from Bacillus stearothermophilus BR219 has been crystallized by vapor-diffusion method. The crystals were grown from a solution containing isopropanol, HEPES and magnesium chloride. The crystals belonged to the monoclinic system with a space group P2 sub(1) and unit cell dimensions of a=69.4Angstrom, b=61.5Angstrom, c=153.1Angstrom and beta =92.6 degree .

Abstract  The synthesis and characterization of three new cofacial biscorroles and three new linked Co(II) porphyrins and Co(III) corroles with the same face to face orientation are described. The biscorroles are represented as (BCS)Co(2), (BCO)Co(2), (BCX)Co(2) while the porphyrin-corrole dyads are represented as (PCA)Co(2), (PCB)Co(2), (PCO)Co(2) where BC represents the Co(III) cofacial biscorroles and PC represents the porphyrin-corrole complexes which are linked to each other by a dibenzothiophene (S), dibenzofuran (O), or 9,9-dimethylxanthene (X) bridge in the case of the corroles and an anthracene (A), biphenylene (B), or dibenzofuran (O) bridge in the case of the mixed macrocycle derivatives. The electrochemical and spectroscopic data on these new bismacrocycles are compared to those of previously reported biscorroles of the type (BCA)Co(2) and (BCB)Co(2). The CO and/or pyridine binding properties of each biscorrole and porphyrin-corrole in CH(2)Cl(2) are also presented. Only one CO ligand is bound axially to each corrole unit of the bismacrocycle but five- and six-coordinate pyridine complexes can be generated for the same compounds, with the exact stoichiometry depending upon the concentration of pyridine in solution. In all cases, the six-coordinate bispyridine corrole complex can be unambiguously identified by a strong diagnostic marker band located at 598-601 nm. The formation constants for pyridine binding to the biscorroles range from log K(1) = 3.14 to 5.08 while log K(2) ranges from 1.10 to 2.61 depending upon the specific spacer. Carbon monoxide binding constants range from log K = 3.6 to 4.0 in the case of the biscorroles and from log K = 3.4 to 4.1 in the case of the porphyrin-corrole dyads. These values also depend on the specific spacer in the complex and, like the pyridine binding constants, decrease in the order BCO > BCA > BCB for the biscorroles and PCO > PCA > PCB for the porphyrin-corrole complexes.

Abstract  2-Amino-5-nitrophenol is used as a colorant in semipermanent hair dyes and in the manufacture of C.I. Solvent Red 8, an azo dye for synthetic resins, lacquers, and wood stains. 2-Amino-5-nitrophenol was nominated for toxicology and carcinogenesis studies by the National Cancer Institute because of widespread human exposure associated with its use in hair dyes. Toxicology and carcinogenesis studies were conducted by administering 2-amino-5-nitrophenol (98% pure) by gavage in corn oil 5 days per week to groups of F344/N rats and B6C3F1 mice of each sex in 16-day, 13-week, and 2-year studies. In the 2-year studies, male and female rats were given doses of 0, 100, or 200 mg/kg and male and female mice were given doses of 0, 400, or 800 mg/kg. Sixteen-day and thirteen-week studies During the 16-day studies, F344/N rats of each sex received 0, 156, 313, 625, 1,250, or 2,500 mg/kg 2-amino-5-nitrophenol by gavage in corn oil vehicle. One of the five males that received 2,500 mg/kg, 1/5 females that received 1,250 mg/kg, and 2/5 females that received 313 mg/kg died before the end of the studies. Final mean body weights of rats that received 1,250 or 2,500 mg/kg were 11% and 30% lower than that of vehicle controls for males and 9% and 13% lower for females. B6C3F1 mice of each sex received doses of 0, 313, 625, 1,250, 2,500, or 5,000 mg/kg 2-amino-5-nitrophenol. Two of five males and 5/5 females that received 5,000 mg/kg, 3/5 males and 3/5 females that received 2,500 mg/kg, 3/5 females that received 1,250 mg/kg, 1/5 females that received 625 mg/kg, and 2/5 male vehicle controls died before the end of the studies. Final mean body weights of chemically exposed mice were not different from those of the vehicle controls. Rats that received 625, 1,250, or 2,500 mg/kg and male mice that received 5,000 mg/kg had loose stools. In 13-week studies, F344/N rats and B6C3F1 mice of both sexes received 0, 100, 200, 400, 800, or 1,600 mg/kg 2-amino-5-nitrophenol by gavage in corn oil. Five of 10 male and 2/10 female rats that received 1,600 mg/kg, 1/10 male and 3/10 female rats that received 800 mg/kg, and 1/10 male rats that received 400 mg/kg died before the end of the studies. Final mean body weights of males that received 400, 800, or 1,600 mg/kg were 10%, 25%, and 43% lower than that of vehicle controls. The final mean body weight of females that received 1,600 mg/kg was 16% lower that of vehicle controls. Four of 10 male and 3/10 female mice that received 1,600 mg/kg died before the end of the 13-week studies. The final mean body weight of male mice that received 1,600 mg/kg was 11% lower than that of vehicle controls; male and female mice that received 1,600 mg/kg appeared lethargic. During the 13-week studies, acute/chronic perivasculitis of vessels of the cecum and colon was observed in rats that received 400, 800, or 1,600 mg/kg and in mice that received 1,600 mg/kg. Two-year studies Body weight and survival Mean body weights of rats receiving 200 mg/kg were 5%-10% lower than those of vehicle controls after week 33 for males and 4%-5% lower than those of vehicle controls after week 93 for females. Survival of male rats was significantly lower than that of vehicle controls after week 99 for the 100 mg/kg dose group and after week 75 for the 200 mg/kg dose group (final survival: vehicle control, 33/50; 100 mg/kg group, 16/50; 200 mg/kg group, 4/50). Survival of female rats was comparable to that of vehicle controls (30/50; 32/50; 29/50). Loose or poorly formed stools were observed for male rats and occasionally for females that received 200 mg/kg. Mean body weights of mice that received 800 mg/kg were 8%-11% lower than those of vehicle controls between weeks 29 and 74 for males and 8%-13% lower than those of vehicle controls after week 69 for females; mean body weights of mice that received 400 mg/kg were greater than those of vehicle controls after week 69 for males and 5%-9% lower than those of vehicle controls after week 69 for females. Survival of mice that received 800 mg/kg was significantly reduced compared with that of vehicle controls after week 20 for males and week 22 for females and was not considered adequate to evaluate a carcinogenic response (final survival--male: vehicle control, 31/50; 400 mg/kg group, 36/50; 800 mg/kg group, 12/50; female: 37/50; 36/50; 10/50). Nonneoplastic and neoplastic effects Pigmentation was present at increased incidences in all groups of chemically exposed animals and was characterized by varying amounts of an orange, granular pigment present in the fibrous connective tissue of the lamina propria, in the submucosa, and around vessels in the submucosa of the cecum and colon. Pigmentation of the rectum was observed at increased incidences in male rats that received 100 mg/kg, male and female rats that received 200 mg/kg, and both groups of chemically exposed mice. No pigmentation was found in the intestines of vehicle control rats or mice. Associated with pigmentation was an increased incidence of acute/chronic inflammation in the cecum and colon of all groups chemically exposed rats and mice; this inflammation was similar to that observed in the 13-week studies but was of greater severity. Acute/chronic inflammation was also present in the rectum of male rats that received 100 mg/kg, male and female rats that received 200 mg/kg, and male mice that received 800 mg/kg. The incidence of pancreatic acinar cell adenomas was significantly increased (P<0.002) in male rats that received 100 mg/kg 2-amino-5-nitrophenol (vehicle control, 1/50; 100 mg/kg, 10/50; 200 mg/kg, 3/49); the increase was considered to be associated with chemical exposure. The reduced survival of male rats that received 200 mg/kg markedly reduced the sensitivity of this group for detecting the presence of neoplasms. The incidences of adenomas or carcinomas (combined) of the preputial or clitoral glands were marginally increased in male or female rats that received 200 mg/kg 2-amino-5-nitrophenol (preputial gland: 3/50; 2/50; 5/50; clitoral gland: 3/50; 3/50; 7/50). Neoplasms found in the intestinal tract of 3/50 male rats that received 100 mg/kg (one leiomyoma of the small intestine, one adenocarcinoma of the jejunum, one leiomyoma of the cecum), 2/50 male rats that received 200 mg/kg (one lipoma and one osteosarcoma of the cecum), and 1/50 female rats that received 200 mg/kg (one leiomyoma of the cecum) were not considered to be the result of chemical exposure. No compound-related neoplasms were found in mice exposed to 2-amino-5-nitrophenol in the 2-year studies. Genetic toxicology 2-Amino-5-nitrophenol was mutagenic in Salmonella typhimurium strains TA98, TA100, and TA1537 when tested in a preincubation protocol with and without exogenous metabolic activation, and it exhibited equivocal mutagenic activity in strain TA1535 in the presence of induced liver S9. 2-Amino-5-nitrophenol induced forward mutations in mouse L5178Y lymphoma cells in the absence of metabolic activation; it was not tested with S9. An increase in chromosomal aberrations and sister chromatid exchanges was observed in cultured Chinese hamster ovary (CHO) cells following incubation with 2-amino-5-nitrophenol both in the presence and absence of exogenous metabolic activation. Data audit The data, documents, and pathology materials from the 2-year studies of 2-amino-5-nitrophenol were audited at the NTP Archives. The audit findings show that the conduct of the studies is documented adequately and support the data and results given in this Technical Report. Conclusions Under the conditions of these 2-year gavage studies, there was some evidence of carcinogenic activity for male F344/N rats that received 100 mg/kg 2-amino-5-nitrophenol, as shown by the increased incidence of acinar cell adenomas of the pancreas. Reduced survival of male F344/N rats that received 200 mg/kg decreased the sensitivity of this group for detecting a carcinogenic response. There was no evidence of carcinogenic activity for female rats that received 100 or 200 mg/kg per day. Marginally increased incidences of preputial or clitoral gland adenomas or carcinomas (combined) occurred in male and female F344/N rats administered 200 mg/kg 2-amino-5-nitrophenol. There was no evidence of carcinogenic activity for B6C3F1 mice that received 400 mg/kg 2-amino-5-nitrophenol; reduced survival of B6C3F1 mice that received 800 mg/kg caused this group to be considered inadequate for detecting a carcinogenic response.

Abstract  a-Methyldopa sesquihydrate is used in the treatment of hypertension; over 20 million prescriptions are written annually for a -methyldopa or a-methyldopa sesquihydrate in the United States. a-Methyldopa sesquihydrate (USP grade, greater than 99% pure) was selected for study because of widespread human exposure and the lack of carcinogenicity studies on this compound. Fourteen-day, 13-week, and 2-year studies were conducted in F344/N rats and B6C3F1 mice. The chemical was administered in feed because human exposure is primarily by the oral route. Short-term studies were performed in bacteria and mammalian cells to evaluate the potential for genetic damage. Fourteen-day and thirteen-week studies In the 14-day studies, the chemical was administered at dietary concentrations of 0 and 6,250-100,000 ppm. All rats receiving 100,000 ppm and 2/5 female rats receiving 50,000 ppm died. All mice lived until the end of the studies. Final mean body weights of dosed male rats were 14%-43% lower than that of controls, and those of dosed female rats were 9%-24% lower. Feed consumption by dosed male and female rats was reduced. Final mean body weights of dosed mice were generally within 10% of those of controls; feed consumption by dosed groups was lower than that by controls during the first week of the studies. In the 13-week studies, the chemical was administered at dietary concentrations of 0 and 3,100-50,000 ppm. Deaths occurred in 4/10 male rats, 7/10 female rats, and 2/10 female mice at 50,000 ppm and in 1/10 female rats at 25,000 ppm. Final mean body weights of dosed rats were 6%-46% lower than those of controls. Feed consumption by dosed rat groups was lower than that by controls. Final mean body weights of male mice at 25,000 and 50,000 ppm and female mice at 50,000 ppm were reduced 12%-19%. Feed consumption by dosed and control mice was comparable. Rats and mice receiving 25,000 and 50,000 ppm exhibited clinical signs of toxicity including lethargy, hyperexcitability, ocular discharge, and rough hair coats. Clinical signs of toxicity were judged to be more severe in dosed male mice than in female mice. Minimal to moderate kidney tubular cell regeneration was seen in male and female rats at 12,500, 25,000, and 50,000 ppm. Bone marrow hypoplasia occurred in male rats at 25,000 and 50,000 ppm and in female rats at 6,300 ppm and higher. Nuclear enlargement (karyomegaly) of the renal corticaltubular epithelium was observed in male and female mice administered 12,500-50,000 ppm; these kidney lesions were judged to be more severe and occurred more frequently at concentrations of 25,000 ppm and higher. Because of kidney lesions, bone marrow responses, and body weight effects at 12,500 ppm and higher and increased deaths and clinical signs at 25,000 and 50,000 ppm, dietary concentrations selected for male and female rats in the 2-year studies were 0, 3,100, and 6,300 ppm. Based on clinical signs, kidney effects, and body weight decreases at 25,000 and 50,000 ppm, dietary concentrations selected for male and female mice in the 2-year studies were 0, 6,300, and 12,500 ppm. Diets containing the chemical at these concentrations were fed to groups of 50 male and 50 female rats and 50 male and 50 female mice for 103 weeks. Two-year studies Body weight and survival Mean body weights of dosed rats were generally 8%-17% lower than those of controls, and mean body weights of dosed mice were generally 5%-22% lower than those of controls throughout the studies. The average amount of a-methyldopa sesquihydrate consumed per day was approximately 110-120 or 230-240 mg/kg per day by low and high dose rats and 830-890 or 1,760-1,800 mg/kg by low and high dose mice. Survival was comparable among dosed and control groups (male rats: control, 28/50; low dose, 26/50; high dose, 27/50; female rats: 35/50; 34/50; 29/50; male mice: 44/50; 42/50; 39/50; female mice: 42/50; 40/50; 38/50). Clinical signs considered to be dose-related included fighting in male rats, irritability in male mice, and rough hair coats in female mice. Nonneoplastic and neoplastic effects Several lesions of the forestomach, including edema, chronic inflammation, epithelial hyperplasia, and ulcers, were seen at low incidences in high dose rats. No forestomach neoplasms occurred. No neoplastic lesions were observed in either male or female rats which were considered related to a-methyldopa sesquihydrate exposure. Nephropathy (control, 3/50; low dose, 21/50; high dose, 32/50), karyomegaly (nuclear enlargement) of cells of the tubular epithelium (0/50; 46/50; 44/50, and cysts (2/50; 10/50; 10/50) were observed in the kidney of dosed female mice. Low incidences of tubular cell hyperplasia (0/50; 1/50; 1/50), tubular cell adenomas (0/50; 2/50; 0/50), and tubular cell adenocarcinomas (0/50; 0/50; 1/50) were observed in male mice. Tubular cell adenomas (3/2,029, 0.15%) and tubular cell adenocarcinomas (3/2,029, 0.15%)are uncommon in untreated control male B6C3F1 mice. No neoplastic lesions in female mice were considered related to a-methyldopa sesquihydrate exposure. Decreased incidences of several site-specific neoplasms were observed in dosed rats and mice; these decreases might have been due in part to decreased weight gain in dosed groups. The decreases occurred in the adrenal medulla of male rats (pheochromocytomas or malignant pheochromocytomas, combined: 21/49; 3/49; 10/50), uterus of female rats (endometrial stromal polyps: 15/50; 5/49; 1/50), liver of male and female mice (hepatocellular adenomas or carcinomas, combined-- male: 15/50; 5/50; 6/50; female: 4/50; 1/50; 0/50), and anterior pituitary gland of female mice (adenoma: 9/49; 4/40; 2/50). The incidences of malignant tumors (male: 19/50; 9/50; 8/50; female: 21/50; 16/50; 12/50) and benign or malignant tumors (combined) (male: 32/50; 15/50; 17/50; female: 33/50; 22/50; 21/50) were reduced in dosed mice. Reproductive studies a-Methyldopa sesquihydrate was administered to male F344/N rats in corn oil by gavage 5 days per week for 65 days at doses of 0, 50, 100, 200, or 400 mg/kg. Decreased body weight was seen in dosed animals. Male rats were mated to untreated female F344/N rats on days 57-61, necropsies were performed on days 65-67, and reproductive toxicity was measured by sperm count, sperm motility, organ weights, hormone levels, and histologic evaluation of the testis. Decreased fertility was observed in males dosed with a-methyldopa sesquihydrate at 200 and 400 mg/kg. Decreases were also seen in sperm count, sperm motility, apparent number of late spermatids, and plasma testosterone levels in males in the 200 and 400 mg/kg groups. This alteration of reproductive function in male rats was found to be reversible after a 13-week recovery period (without dosing). The decreased fertility observed after a-methyldopa sesquihydrate administration was probably due in part to the decreases in plasma testosterone levels. Genetic toxicity a-Methyldopa sesquihydrate was not mutagenic when tested with or without exogenous metabolic activation with a preincubation protocol in four strains of Salmonella typhimurium (TA97, TA98, TA100, or TA1535). No increase in chromosomal aberrations or sister chromatid exchanges was observed in Chinese hamsterovary (CHO) cells exposed to a-methyldopa sesquihydrate with or without S9. Data audit The data, documents, and pathology materials from the 2-year studies of a-methyldopa sesquihydrate have been audited. The audit findings show that the conduct of the studies is documented adequately and support the data and results given in this Technical Report. Conclusions Under the conditions of these 2-year feed studies, there was no evidence of carcinogenic activity of a-methyldopa sesquihydrate for male or female F344/N rats fed diets containing 3,100 or 6,300 ppm. There was equivocal evidence of carcinogenic activityof a-methyldopa sesquihydrate for male B6C3F1 mice, as shown by three dosed mice having uncommon tubular cell tumors of the kidney. There was no evidence of carcinogenic activity of a -methyldopa sesquihydrate for female B6C3F1 mice fed diets containing 6,300 or 12,500 ppm. Nonneoplastic lesions of the kidney including karyomegaly were observed in dosed female mice. Decreased incidences of several tumor types (in the adrenal gland in male rats, uterus in female rats, liver in male and female mice, and anterior pituitary gland in female mice) were considered related to a-methyldopa sesquihydrate exposure.

Abstract  Five chemicals of industrial and agricultural relevance—ethylene dibromide, ethylene dichloride, propylene dichloride, allyl alcohol and sulphallate—were tested for their ability to induce reverse mutations in Salmonella typhimurium and forward mutations in Streptomyces coelicolor and Aspergillus nidulans. Ethylene dibromide was positive in all the genetic systems employed; sulphallate gave a positive response, to different degrees, in all the microorganisms; ethylene dichloride was weakly active in S. typhimurium following microsomal activation; propylene dichloride was detected as a direct acting mutagen in S. typhimurium and A. nidulans but not in S. coelicolor; allyl alcohol was completely negative in all test systems.