CHLORDIMEFORM EXPLANATION Chlordimeform was reviewed and evaluated for an acceptable daily intake by the Joint Meetings in 1971, 1975, 1978, 1979 and 1980 (Annex 1, FAO/WHO, 1972a, 1976a, 1979a, 1980a and 1981a). A toxicological monograph was prepared by the Joint Meeting in 1971 (Annex 1, FAO/WHO, 1972b) and monograph addenda were prepared in 1975, 1978, 1979, and 1980 (Annex 1, FAO/WHO, 1976b, 1979b, 1980b, and 1981b). A temporary acceptable daily intake (TADI) of 0-0.01 mg/kg b.w. was established in 1971 and reduced to 0-0.0001 in 1978. Further evaluations carried out in 1979 and 1980 did not modify the TADI. The 1980 Meeting required for review at the present meeting a report on continued surveillance and epidemiological studies of occupationally exposed workers in both industry and agriculture. A confirmatory long-term animal bioassay using a third species for evaluation of potential carcinogenic hazard was considered desirable. A considerable amount of additional information, not all relevant to the above requests, was evaluated by the Meeting and is presented in this monograph addendum. EVALUATION FOR ACCEPTABLE DAILY INTAKE BIOLOGICAL DATA Biochemical Aspects Effects on enzymes and other biochemical parameters In a study to investigate the effects of chlordimeform on hepatic enzymes in rats and mice, groups of eight male and eight female Tif:Magf (SPF) mice and Sprague-Dawley-derived Tif:RAI f (SPF) rats were treated by gastric intubation with 0, 50, 100 and 150 mg/kg b.w. chlordimeform in 0.9% saline solution (1 ml/100 g b.w.) for seven consecutive days. The animals were then fasted for 24 hours before sacrifice. The following parameters were investigated in hepatic microsomal fractions: benzo(a)pyrene hydroxylase, ethoxycoumarin O-de-ethylase ethylmorphine N-demethylase, cytochrome P-450 content, NADPH cytochrome P-450 reductase, UDP-glucuronyl transferase, and microsomal epoxide hydrolase. Glutathione S-transferase was measured in 100,000xg supernatants. Chlordimeform treatment induced several hepatic drug-metabolising enzymes with some species and/or sex specificity. Relative liver weights were increased in female rats and mice in a dose-dependent manner. Cytochrome P-450 content was increased in all cases but cytochrome P-450 reductase activity was increased only in the highest dose in male rats and mice and in the lowest and highest doses only in female mice. Ethylmorphine N-demethylase was induced in a dose- dependent manner in male mice but only at the highest dose in female mice. Ethoxycoumarin O-de-ethylase was induced in dose-dependent manner in male and female rats but only at high doses in both sexes of mice. Benzo(a)pyrene hydroxylase was increased in a dose-dependent manner in female rats and mice but only at the mid-dose in male mice. UDP-glucuronyl transferase was induced in rats of both sexes and female mice in a dose-dependent manner but male mice exhibited no induction. Dose-dependent increases of expoxide hydrolase and glutathione S-transferase occurred in male and female rats and female mice. (Bentley et al., 1985a). The results of these investigations clearly indicate that chlordimeform induces the activity of several hepatic enzymes but reveal no clear distinctions between rats and mice. The effect of acute and repeated chlordimeform treatment on rat hepatic microsomal enzymes has been examined following acute or repeated dosing. Groups of 6 male and 6 female Sprague-Dawley rats received either a single intraperitoneal injection of chlordimeform (100 mg/kg) 60 minutes prior to sacrifice or daily injections (75 mg/kg) for 4 days. Control animals received equivolume injections of normal saline (1 ml/kg). The duration of zoxazolamine-induced paralysis (70 mg/kg i.p.) or pentobarbitone-induced hypnosis (40 mg/kg i.p.) were assessed in the latter group. Hepatic microsomal preparations were utilized to assay the following enzymatic activities: ethylmorphine N-demethylase, aniline hydroxylase, p-nitroanisole-O-demethylase and NADPH cytochrome C reductase. Hepatic microsomal cytochrome P-450 content was estimated and the spectral binding of chlordimeform (2.1 mM), aniline (20 mM) and hexobarbital (10 mM) to hepatic microsomes was studied. It was found that acute chlordimeform exposure prolonged zoxazolamine paralysis and pentobarbitone hypnosis. However, after repeated exposure, the duration of zoxazolamine paralysis was significantly reduced whilst the duration of pentabarbitone hypnosis remained unchanged. Significant sex-related difference in hepatic metabolism were found. In male rats, ethylmorphine N-demethylation was significantly reduced in acutely treated animals and to a lesser extent in the repeatedly exposed group. Repeated exposure caused a modest reduction in aniline hydroxylation but did not affect the metabolism of p-nitranisole. For female rats, however, either acute or repeated chlordimeform treatment had little effect on ethylmorphine N-demethylation and p-nitroanisole demethylation whilst aniline was metabolised to a lesser extent following both treatment regimens. These results suggest that the hepatic microsomal enzymes of male rats are significantly more responsive to chlordimeform exposure than are those of females. In acutely-treated rats, hepatic microsomal NADPH cytochrome C reductase activity, cytochrome P-450 content and the spectral binding of hexobarbitone and aniline were significantly reduced. However, only the spectral binding of hexobarbitone was significantly reduced in rats repeatedly exposed to chlordimeform. Chlordimeform was found to produce a characteristic Type I difference spectrum when added to rat liver microsomes. The authors concluded that chlordimeform bound to cytochrome P-450 at non-active sites, producing a change in protein conformation (Budris et al., 1983). Special studies on mutagenicity Chlordimeform and its principal metabolites, 4-chloro-2-toluidine and N-formyl-2-toluidine, were variably active in a range of in vitro assays. In vivo, however, chlordimeform was inactive but the metabolites were each positive in one assay. Results are summarised in Table 1. Special studies on macromolecular binding Species difference in the DNA-binding of the metabolite 4-chloro-2-toluidine were investigated in rats and mice in vivo and in vitro. l4C-Ring labelled metabolite was dosed daily at 25 mg/kg to male Tif:MAG f (SPF) mice, and Sprague-Dawley derived Tif:RAI f (SPF) rats, by gastric intubation. Animals were held for 20 hours before sacrifice. The radioactivity bound to purified DNA isolated from liver homogenates was found to increase with total dose in both rats and mice. DNA binding in mice was about twice that in rats. Covalent binding of 4-chloro-2-toluidine to calf thymus DNA was studied in vitro after incubation with liver fractions from rats and mice. Mouse liver fractions produced more metabolites which bound to DNA than did those prepared from rat liver. Binding was catalysed by active liver homogenates and microsomal fractions and was NADPH-dpendent. Pretreatment with known inducers of cytochrome P-450 (phenobarbitone, 3-methylcholanthrene, and arochlor 1254) was without effect. The patterns of adducts produced in rat and mouse liver in vivo and by incubation of calf thymus DNA in vitro with hepatic subcellular fractions of each species were analysed chromatographically. The patterns were qualitatively similar, the same metabolites being formed in each case. Significant quantitative differences occurred with two metabolites only (Bentley et al., 1985b). Species differences in the toxicity of 4-chloro-2-toluidine were further investigated. 14C-4-Chloro-2-toluidine (25 mg/kg) was administered in aqueous solution by gastric intubation to male Tif:MAG f(SPF) mice and Sprague-Dawley derived Tif:RAI f (SPF) rats. Urinary Table 1: Results of mutagenicity assays on chlordimeform and its metabolites Test system Test Test substance Concentrations Results Reference Object (purity) used Studies on microorganisms Salmonella typhimurium/ TA98 chlordimeform -S9: 0.1,1,10.100,1000 µg/0.1 ml - Arni & Müller, microsome TA100 HCl* +S9: 0.1,1,10,100,1000,2000 - 1976a TA1535 µg/0.1 ml - TA1537 - TA98 N-formyl-4- ±S9: 0.1,1,10,100,1000 µg/O.1 ml - Arni & Müller, TA100 chloro-2- +(with S9 only) 1976b TA1535 toluidine* - TA1537 - TA98 4-chloro-2- ±S9: 0.1,1,10,100,1000 µg/0.1 ml +(with S9 only) Arni & Müller, TA100 toluidine +(with S9 only) 1976b TA1535 HCl* - TA1537 - Salmonella typhimurium/ TA98 chlordimeform single oral dose of 50, 100, - Arni & Müller, Intrasanguine host- TA100 HCl (99.9%) 200 mg/kg in mice - 1983a mediated assay TA1535 - TA98 4-chloro-2- single oral dose of 250,500, - Arni & Müller, TAlO0 toluidine 1000 mg/kg in mice - 1983b TA1535 HCl (99.9%) - Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used Saccharomyces cerevisiae/ D7 chlordimeform ±S9: 80,400,2000,10000 µg/ml inhibition of Arni & Müller, microsome HCl (99.9%) ±S9: 15,45,125,405 µg/ml growth above 1983c 400 µg/ml D7 4-chloro-o- ±S9: 80,400,2000,10000 µg/ml inhibition of Arni & Müller, toluidine HCl ±S9: 3.2,10,30,90 µg/ml growth at all 1983d (99.9%) conc. +(at 30, 90 µg/ml) Salmonella typhimurium/ TA98 chlordimeform* ±S9: 100 µg/ml - Konopka & microsome TA100 - Heymann, TA1535 - 1977 TA1537 - TA1538 - TA98 4-chloro-2- -S9: 500 µg/ml +(with S9 at 250 Konopka & toluidine µg/ml) Heymann, 1977 TA100 +S9: 10,250,500 µg/ml +(with S9 at 10 µg/ml) TA1535 - TA1537 - TA1538 - TA98 2-chloro-N- -S9: 500 µg/ml - Konopka & TA100 formyl-2- +S9: 100, 500 µg/ml +(with S9 at Heymann, 1977 toluidine* 100 µg/ml) TA1535 - TA1537 - TA1538 - Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used TA98 chlordimeform ±S9: 100,500,1000,2000 µg/plate - Meucke TA100 HCl - et el., 1979 TA98 4-chloro-2- ±S9: 0.1,1,5,10,25,50,100,1000 +(with S9 only) Meucke TA100 toluidine HCl 2000 µg/plate +(with S9 above et al., 1979 100 µg only) TA100 N-formyl-4- ±S9: 0.1-2000 µg/plate - Meucke chloro-2- et el., 1979 toluidine TAl00 4-chloro-2- ±S9: 10-2000 µg/plate - Meucke toluidyl-N,N- et el., 1979 dimethy iormamide Salmonella typhimurium/ TA100 4-chloro-2- ±S9: 10-2000 µg/plate - Meucke microsome toluidyl-N,N- et al., 1979 methyl formamide TA100 4-chloro-2- ±S9: 10-2000 µg/plate - Meucke toluidyl- et al., 1979 formamide TA100 4-chloro-2- ±S9: 0.1-2000 µg/plate *(above 25 µg Meucke methylphenyl- with S9) et al., 1979 hydroxylamine +(above 50 µg without S9) Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used TA100 5-chloro-2- ±S9: 0.1-2000 µg/plate *(above l0 µg Meucke nitroso- with S9 only) et al., 1979 toluene TA100 4-chloro-acetyl- ±S9: 0.1-2000 µg/plate - Meucke 2-toluidine et al., 1979 TA100 4-chloro-acetyl- ±S9: 0.1-2000 µg/plate - Meucke N-hydroxy-o- et al., 1979 toluidine TA100 4,4'-dichloro- ±S9: 0.1-2000 µg/plate - Meucke 2,2'-dimethyl- et al., 1979 azobenzene TA100 4,4'-dichloro- ±S9: 0.1-2000 µg/plate - Meucke 2,2'-dimethyl- et al., 1979 azobenzene- N-oxide TA98 chlordimeform -S9: 1,5,25,125,625 µg/plate - Rashid TA100 (analytical +S9: 5,10,50,250,1250 µg/plate - et al., 1984 TA1535 grade) - TA1537 - TA1538 - TA98 4-chloro-N- -S9: 1,5,25,125,325 µg/plate - Rashid TAlO0 formyl-2- - et al. 1984 TA1535 toluidine* +(325 µg/plate) TA1537 - TA1538 - Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used TA98 4-chloro-2 -S9: 1,5,25,125,325 µg/plate - Rashid TA100 toluidine - et al. 1984 TA1535 (99%) - TA1537 - TA1538 - Eschericia coli/ WP2 chlordimefom ±S9: 250,500,1000, - Rashid microsome WP2uvrA (analytical 2000 µg/plate - et al., 1984 WP67 grade) - CM611 - CM571 - WP2 4-chloro-N- ±S9: 250,500,1000, - Rashid WP2uvrA formyl-2- 2000 µg/plate - et al., 1984 WP67 toluidine* - CM611 - CM571 - WP2 4-chloro-2- ±S9: 250,500,1000, - Rashid WP2uvrA toluidine 2000 µg/plate - et al., 1984 WP67 (99%) - CM611 - CM571 - Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used In vitro assays Cell transformation BALB/ chlordimeform 0.063,0.125,0.25,0.5,1.0 µg/ml +(not dose- Beilstein & assay 3T3 HCL (99.9%) related) Müller, 1983 Mouse lymphoma test L5178Y/ chlordimeform -S9: 42.5-1700 µg/ml -(cytotoxicity Beilstein & TK+/- HCl* above 850 µg/ml) Müller, 1984a +S9: 75-3000 µg/ml -(cytotoxicity above 1800 µg/ml) L5178Y/ 4-chloro-2- -S9: 37.5-600 µg/ml -(cytotoxicity Bellserin & TK+/- toluidine HCl above 450 µg/ml) Müller, 1984b * +S9: 31.3-500 µg/ml + Cell transformation BALB/ 4-chloro-2- 2.25, 4.5, 9, 18, 36 µg/ml + Bellstein & assay 3T3 toluidine HCl Müller, 1984c (99.9%) DNA repair test rat chlordimeform 5, 25, 125, 625 µg/ml - Puri & Müller, hepatocytes HCl (99.9%) 1983a rat 4-chloro-2- 0.61, 3.1, 15.7, 78.5 µg/ml +(dose-related) Puri & Müller, hepatocytes toluidine HCl 1983b (99.9%) DNA repair test CRL chlordimeform 2, 10, 50, 250 µg/ml - Puri & Müller, human lymphocytes 1121 HCl (99-9%) 1983c CRL 4-chloro-2- 1.25, 6.25, 31.25, 156.25 µg/ml - Puri & Müller, 1121 toluidine HCl 1983d (99.9%) Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used Mouse lymphoma cells/ L5178Y 4-chloro-2- single oral dose of 330 mg/kg - (no positive Strasser & host-mediated toluidine HCl* in mice control) Müller, 1983a assay L5178Y N-formyl-4- single oral dose of 300 mg/kg - (no positive Strasser & chloro-2- in mice control Müller, 1983b toluidine* Mouse lymphoma cells/ L5178Y 4-chloro-o- 111, 255 µg/ml + (no positive Strasser & point mutation toluidine HCl* control) Müller, 1984a L5178Y N-formyl-4- 213,640 µg/ml + (no positive Strasser & chloro-2- control) Müller, 1984b toluidine* In vivo assays Chromosomal/germinal spermatogonia N-formyl-4- 1 oral dose o£ 80, 160, or - Arni epithelium chloro-2- 320 mg/kg in mice et al., 1983a totuidine* spermatocytes chlordimeform 5 oral doses of 18, 36, or - Arni HCl* 72 mg/kg in mice et al., 1983b spermatocytes N-formyl-4- 5 oral doses of 80, 160, or + (chromosomal Arni & Müller, chloro-2- 320 mg/kg in mice aberration, not 1983e toluidine* dose-related) Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used Dominant lethal 4-chloro-2- single oral dose of - Fritz toluidine HCl* 110 or 330 mg/kg in mice et al., 1978 chlordimeform * single oral dose of - Fritz, 1978a 22 or 66 mg/kg in mice N-formyl-4- single oral dose of - Fritz, 1978b chloro-2- 105 or 315 mg/kg in mice toluidine * Chromosomal/germinal spermatogonia chlordimeform 5 oral doses of 9, 18, 22, 36, - Hool epithelium HCL* and 66 mg/kg in mice et al., 1983 Chromosomal/somatic bone N-formyl-4- 2 oral doses of 300, 600, and + (not seen in Hool & Arni, cells marrow chloro-2- 1200 mg/kg in Chinese hamster repeat 1983a toluidine* experiment) bone 4-chloro-2- 2 oral doses of 100,200,237,356, + Hool & Arni, marrow toluidine HCl* 533,800 mg/kg in Chinese hamster 1983b Chromosomal/germinal spermatogonia 4-chloro-2- 5 oral doses of 85, 125, 170, - Hool & Arni, epithelium toluidine HCI* 250, 340, 500 mg/kg in mice 1983c spermatocytes 4-chloro-2- 5 oral doses of 85, 125, 170, - Hool & Arni, toluidine HCl* 250, 340, 500 mg/kg in mice 1983d Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used Sister chromatid bone chlordimeform single oral dose of 31, 62, 324 - Hool & Armi, exchange marrow HCl (99.9%) mg/kg in Chinese hamster 1983e bone 4-chloro-2- single oral dose of 100, 200, - Hool & Arni, marrow toluidine HCl 400 mg/kg in Chinese hamsters 1983f (99.9%) Chromosomal/somatic bone chlordimeform 2 oral doses of 60, 120, 240 - Hool & Müller, cells marrow HCl* mg/kg in Chinese hamster 1978 Heritable translocation male chlordimeform* 49 daily oral doses of 120 mg/kg - Lang & Adler, mice 1982 male N-formyl-4- 49 daily oral doses of 100 mg/kg - Lang & Adler, mice chloro-2- 1982 toluidine* male 4-chloro-2- 49 daily oral doses of 200 mg/kg - Lang & Adler, mice toluidine* 1982 Mammalian spot test C57BL/ chlordimeform 3 oral doses of 160 mg/kg - Lang, 1984 6J mice genotype a/a b/+;cch N-formyl-4- 3 oral doses of 100 mg/kg - Lang, 1984 p/++; chloro-2- dse/++; toluidine* s/+ Table 1: (Con't) Test system Test Test substance Concentrations Results Reference Object (purity) used 4-chloro-2- 3 oral doses of 100 mg/kg +(spots of Lang, 1984 toluidine* genetic relevance) Nucleus anomaly/ bone chlordimeform 2 oral doses of 60, 120, 240 - Langauer & somatic nuclei marrow HCI* mg/kg in Chinese hamsters Müller, 1977 bone N-formyl-4- 2 oral doses of 300, 600, 1200 - Langauer & marrow chloro-2- mg/kg in Chinese hamsters Müller, 1978a toluidine* bone 4-chloro-2- 2 oral doses of 100, 200, 400 - Langauer & marrow toluidine* mg/kg in Chinese hamsters Müller, 1978b * Purity not specified excretion of radioactivity was monitored daily until sacrifice. Covalent binding of radioactivity to hepatic DNA, RNA and protein was measured 6, 12, 20 and 68 hours after treatment. In each case, the extent of binding to mouse DNA significantly exceeded that to rat DNA but binding to mouse RNA and protein exceeded that to rat DNA and protein. The effect of 4-chloro-2-toluidine upon the incorporation of 3H-thymidine into capillary endothelial cells was also studied. Male rats and mice were dosed orally with 4-chloro-2-toluidine (25 mg/kg/day) and received subsequently 3H-thymidine by i.p. administration at varying intervals. The incorporation of radioactivity into blood capillary endothelial cell nuclei was studied by autoradiography. Between 500 to 1500 nuclei per animal were assessed. It was found that the incorporation of 3H-thymidine was not elevated in treated animals when compared to controls (Bentley et al., 1985c). Observations in humans Information was submitted on the results of monitoring the urine of more than 100 workers engaged in chlorimeform production and packaging in 1976. In more than 800 individual urine samples, total urinary levels ranged from 0.05-50 ppm. Microscopic haematuria was not detectable, suggesting that it may not occur at these levels of excretion (Barnett, 1979). Information was also submitted on the results of urinary monitoring of workers engaged in chlordimeform application to cotton in seven countries (Limmer, 1985). As the temporal relationship between exposure and urine sampling was not established, it was not possible to relate this information to actual levels of exposure. In the period 1980-1984, four separate incidents resulting in 7 cases of frank haematuria following industrial exposure occurred in the USA. Chemical cystitis, confirmed by cystoscopy and biopsy, was diagnosed in one case while non-specific bladder mucosal lesions was found in another. Six cases required hospitalisation but all resolved after cessation of exposure (Barnett, 1985). In the same period, no cases of chlordimeform-induced haematuria occurred at manufacturing plants in Switzerland and West Germany or formulation plants in Australia, Columbia, Central America, Mexico and the USA. No cases of haematuria reportedly resulted from application or use of chlordimeform in the field. (Reckefus and Kossman, 1985; Pfister and Dubach, 1985). Twenty-one cases of haemorrhagic cystitis have been reported in workers exposed to chlordimeform wastes and in those drinking contaminated water (Morgan and Gillen, 1982). COMMENTS Chlordimeform has been found to induce haemangiosarcomas in mice but not in rats (JMPR, 1980; Annex 1, FAO/WHO, 1981a). 4-Chloro-2- toluidine (previously termed 4-chloro-O-toluidine), a metabolite of chlordimeform, also produces haemangiosarcomas in mice but not in rats (IARC, 1983). Data reviewed by the present meeting indicated that chlordimeform induced the activity of several hepatic drug metabolising enzymes but the observed biological differences could not be attributed to the results of either in vivo or in vitro studies. Studies of macromolecular binding of 4-chloro-2-toluidine to RNA and DNA of rat and mouse tissues in vitro and in vivo also could not explain the observed differences in response to this compound, nor could a study of its effect on the incorporation of 3H-thymidine into capillary endothelial cells. Chlordimeform was without mutagenic activity in various cellular systems but gave positive results in a cell transformation assay. The metabolites 4-chloro-2-toluidine and N-formyl-4-chloro-2-toluidine were positive in several reverse mutation assays but only with metabolic activation; the former metabolite was also positive in mouse lymphoma, cell transformation and DNA repair assays. Both produced chromosomal anomalies in at least one in vivo assay. Occupational studies indicate that haematuria and cystitis have occurred following incidents of relatively high exposure. Exposed workers readily absorb chlordimeform and the excretion of 4-chloro-2- toluidine can be monitored. Data were submitted on the results of extensive urinary monitoring of chlordimeform applicators in seven countries. Results were variable but could not be related to exposure adequately, as information on the timing of exposure and sample collection was not provided. It is of interest to note that a daily excretion of 1.5 litres of urine containing 0.5 mg/1 of 4-chloro-2-toluidine by a 60 kg individual approximates to absorption of 0.017 mg/kg body weight of chlordimeform. Epidemiological data were not submitted. The Meeting was advised by the submitters of the data that chlordimeform is used only on cotton and that no other uses are anticipated. The Meeting recommended that the use of chlordimeform be restricted to cotton production. As the Meeting considered that the available information partially met the requirement of the 1980 Joint Meeting, it decided to extend the temporary ADI. TOXICOLOGICAL EVALUATION LEVEL CAUSING NO TOXICOLOGICAL EFFECT Rat: 2 ppm in the diet, equivalent to 0.1 mg/kg b.w. Dog: 250 ppm in the diet, equivalent to 6.25 mg/kg b.w. ESTIMATE OF TEMPORARY ACCEPTABLE DAILY INTAKE FOR MAN 0.0001 mg/kg b.w. REQUIRED (by 1987) Interpretable epidemiological and urinary monitoring data on occupationally-exposed workers. DESIRED 1. Confirmatory long-term animal bioassay using a third species for evaluating the potential carcinogenic hazard. 2. Further observations in man. REFERENCES Arni, P., Hool, G., & Müller, D. CGA 72'651: Chromosome studies in (1983a) male germinal epithelium (mouse spermatogonia). Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P., Hool, G., & Müller, D. C8513: Chromosome studies in male (1983b) germinal epithelium (mouse spermatogonia). Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. C8513: Salmonella/mammalian mutagenicity test. (1976a) Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. CGA 72'651: Salmonella/mammalian-microsome (1976b) mutagenicity test. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. CGA 72'647: Salmonella/mammalian-microsome (1976c) mutagenicity test. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. C8513: Intrasanguine host-mediated assay with (1983a) S. typhimurium. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. CGA 72'647: Intrasanguine host-mediated assay (1983b) with S. typhimurium. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. C8513: Saccharomyces cerevisiae D7/mammalian- (1983c) microsome mutagenicity test in vitro. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. CGA 72'647: Saccharomyces cerevisiae (1983d) D7/mammalian-microsome mutagenicity test in vitro. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Arni, P. & Müller, D. CGA 72'651 pure: Chromosome studies in male (1983e) germinal epithelium (mouse spermatocytes). Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Barnett, J.W. Letter to California Department of Food and Agriculture (1979) from Ciba-Geigy Agricultural Div., Greenborough, NC, USA. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Barnett, J.W. Letter to Ciba-Geigy Ltd., Basel, Switzerland from Ciba (1985) Geigy Agricultural Division, Greenborough, NC. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Beilstein, P. & Müller, D. C8513; BALB/3T3 cell transformation assay. (1983) Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Beilstein, P. & Müller, D. C8513; L1578Y/TK+/- mouse lymphoma (1984a) mutagenicity test. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Beilstein, P. & Müller, D. CGA 72'647: L1578Y/TK+/- mouse lymphoma (1984b) mutagenicity test. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Beilstein, P. & Müller, D. CGA 72'647: BALB/3T3 cell transformation (1984c) assay. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Bentley, P., Staubli, W., Bieri, F., Muecke, W., & Waechter, F. (1985a) Induction of hepatic drug metabolising enzymes following treatment of rats and mice with chlordimeform. Unpublished report from Central Toxicology Unit and Agricultural Division, Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Bentley, P., Bieri, F., Waechter, F., Staubli, W., & Muecke, W.. (1985b) Species differences in the toxicity of 4-chloro-o-toluidine to rats and mice. Covalent binding to DNA assessed in vivo and in vitro. Unpublished report from Central Toxicology Unit and Agricultural Division, Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Bentley, P., Bieri, F., Muecke, W., Waechter, F., & Staubli, W. (1985c) Species differences in the toxicity of 4-chloro-o-toluidine to rats and mice. Covalent binding to hepatic macromolecules and hepatic non-parenchymal cell DNA and an investigation of effects upon the incorporation of (3H)-thymidine into capillary endothelial cells. Unpublished report from Central Toxicology Unit and Agricultural Division, Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Budris, D.M., Yim, G.K.W., Carlson, G.P., & Schnell, R.C. Effect of (1983) acute and repeated chlordimeform treatment on rat hepatic microsomal drug metabolising enzymes. Toxicology Letters 18, 63-71. Fritz, H., Becker, H., & Müller, D. CGA 72'647: Dominant lethal study (1978) (mouse). Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Fritz, H. C8513: Dominant lethal study (mouse). Unpublished report (1978a) from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Fritz, H. CGA 72'651: Dominant lethal study (mouse). Unpublished (1978b) report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. Hool, G., Bulstein, P., & Arni, P. C8513: Chromosome studies in male (1983) germinal epithelium mouse spermatogonia. Unpublished report from Ciba-Geigy Ltd., Basel, Switzerland. Submitted to WHO by Ciba-Geigy Ltd. and Schering Aktiengesellschaft. 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See Also: Toxicological Abbreviations Chlordimeform (EHC 199, 1998) Chlordimeform (ICSC) Chlordimeform (WHO Pesticide Residues Series 1) Chlordimeform (WHO Pesticide Residues Series 5) Chlordimeform (Pesticide residues in food: 1978 evaluations) Chlordimeform (Pesticide residues in food: 1979 evaluations) Chlordimeform (Pesticide residues in food: 1980 evaluations) Chlordimeform (Pesticide residues in food: 1987 evaluations Part II Toxicology) Chlordimeform (IARC Summary & Evaluation, Volume 30, 1983)